From 99ac66e49e90277e2420945628d0aae55bce2336 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 15:36:33 -0300
Subject: [PATCH 01/17] =?UTF-8?q?Insere=20a=20classe=20`thumbImg`=20para?=
 =?UTF-8?q?=20que=20a=20miniatura=20fique=20ajustada=20no=20modal=20que=20?=
 =?UTF-8?q?cont=C3=A9m=20todos=20os=20elementos=20gr=C3=A1ficos=20(o=20mod?=
 =?UTF-8?q?al=20com=20as=20abas=20e=20que=20abre=20ao=20clicar=20no=20menu?=
 =?UTF-8?q?=20flutuante=20com=20...=20)?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl | 5 +++--
 1 file changed, 3 insertions(+), 2 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 552203825..9d771af34 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -308,7 +308,7 @@
             <xsl:apply-templates select="fig[@xml:lang=$TEXT_LANG]" mode="tab-content-label-and-caption"></xsl:apply-templates>
         </div>
     </xsl:template>
-    <xsl:template match="fig[@id]" mode="tab-content">
+    <xsl:template match="fig" mode="tab-content">
         <!--
             cria no conteúdo da ABA "Figures" a miniatura e legenda de uma figura
             (cujo label e caption estão em apenas um idioma)
@@ -328,7 +328,7 @@
         <xsl:variable name="figid">
             <xsl:choose>
                 <xsl:when test="@id"><xsl:value-of select="@id"/></xsl:when>
-                <xsl:otherwise>IDMISSING</xsl:otherwise>
+                <xsl:otherwise></xsl:otherwise>
             </xsl:choose>
         </xsl:variable>
         <xsl:variable name="location">
@@ -339,6 +339,7 @@
                 <div>
                     <xsl:choose>
                         <xsl:when test="$location != ''">
+                            <xsl:attribute name="class">thumbImg</xsl:attribute>
                             <img>
                                 <xsl:attribute name="src"><xsl:value-of select="$location"/></xsl:attribute>
                             </img>

From 9c212c491012f894eb2b49a617c02a5de70ccaf1 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 16:46:41 -0300
Subject: [PATCH 02/17] =?UTF-8?q?Faz=20ajustes=20para=20considerar=20figur?=
 =?UTF-8?q?as=20que=20n=C3=A3o=20tem=20`@id`?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/article-text-fig.xsl      |  2 +-
 .../catalogs/htmlgenerator/v2.0/html-modals.xsl  | 16 +++++++++++++++-
 2 files changed, 16 insertions(+), 2 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl b/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
index 3ec631024..a3105f988 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
@@ -50,7 +50,7 @@
         <xsl:apply-templates select="." mode="label-caption-thumb"/><br/>
     </xsl:template>
 
-    <xsl:template match="fig[@id] | fig-group[@id]" mode="figure-id">
+    <xsl:template match="fig | fig-group[@id]" mode="figure-id">
         <xsl:value-of select="@id"/>
     </xsl:template>
 
diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 9d771af34..c9a17463d 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -90,7 +90,7 @@
 
     <xsl:template match="front | body | back | sub-article" mode="fig-individual-modal">
         <!-- cria um modal para cada figura existente no body-->
-        <xsl:apply-templates select=".//fig-group[@id] | .//fig" mode="modal"></xsl:apply-templates>
+        <xsl:apply-templates select=".//*[fig]" mode="fig-modal"></xsl:apply-templates>
     </xsl:template>
 
     <xsl:template match="article" mode="modal-grouped-figs-tables-schemes">
@@ -268,6 +268,20 @@
         <xsl:apply-templates select=".//*[fig]" mode="figs-tab-content"/>
     </xsl:template>
 
+    <xsl:template match="*[fig]" mode="fig-modal">
+        <!--
+        cria o conteúdo de uma figura no Modal na aba "Figures"
+        -->
+        <xsl:choose>
+            <xsl:when test="name()='fig-group'">
+                <xsl:apply-templates select="." mode="modal"/>
+            </xsl:when>
+            <xsl:otherwise>
+                <xsl:apply-templates select=".//fig" mode="modal"/>
+            </xsl:otherwise>
+        </xsl:choose>
+    </xsl:template>
+
     <xsl:template match="*[fig]" mode="figs-tab-content">
         <!--
         cria o conteúdo de uma figura no Modal na aba "Figures"

From 807d4e80a62e9648c56796182ae2c6edebfd506e Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 17:19:03 -0300
Subject: [PATCH 03/17] =?UTF-8?q?Junta=20os=20templates=20que=20tem=20cont?=
 =?UTF-8?q?e=C3=BAdo=20id=C3=AAntico?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 60 ++++++++++---------
 1 file changed, 31 insertions(+), 29 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index c9a17463d..a4132a0ff 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -312,25 +312,21 @@
         <xsl:apply-templates select=".//disp-formula[@id]" mode="tab-content"/>
     </xsl:template>
 
-    <xsl:template match="fig-group[@id]" mode="tab-content">
+    <xsl:template match="fig-group[@id] | fig" mode="tab-content">
         <!--
-            cria no conteúdo da ABA "Figures" a miniatura e legenda de uma figura
-            (cujo label e caption estão em mais de um idioma)
-        -->
-        <div class="row fig">
-            <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
-            <xsl:apply-templates select="fig[@xml:lang=$TEXT_LANG]" mode="tab-content-label-and-caption"></xsl:apply-templates>
-        </div>
-    </xsl:template>
-    <xsl:template match="fig" mode="tab-content">
-        <!--
-            cria no conteúdo da ABA "Figures" a miniatura e legenda de uma figura
-            (cujo label e caption estão em apenas um idioma)
+            Para fig-group e fig, cria no conteúdo da ABA "Figures":
+            - a miniatura
+
+            Para fig-group:
+            - legendas de uma figura (label e caption em mais de um idioma)
+
+            Para fig:
+            - legenda de uma figura (label e caption em um idioma)
         -->
         <div class="row fig">
             <!-- miniatura -->
             <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
-            <!-- legenda -->
+            <!-- legenda(s) -->
             <xsl:apply-templates select="." mode="tab-content-label-and-caption"></xsl:apply-templates>
         </div>
     </xsl:template>
@@ -369,6 +365,13 @@
         </div>
     </xsl:template>
 
+    <xsl:template match="fig-group" mode="tab-content-label-and-caption">
+        <!--
+            cria as legendas de uma figura no conteúdo da ABA "Figures"
+        -->
+        <xsl:apply-templates select="fig" mode="tab-content-label-and-caption"/>
+    </xsl:template>
+
     <xsl:template match="fig" mode="tab-content-label-and-caption">
         <!--
             cria a legenda de uma figura no conteúdo da ABA "Figures"
@@ -378,23 +381,15 @@
         </div>
     </xsl:template>
 
-    <xsl:template match="table-wrap-group[table-wrap]" mode="tab-content">
+    <xsl:template match="table-wrap-group[table-wrap] | table-wrap[not(@xml:lang)]" mode="tab-content">
         <!--
-            cria no conteúdo da ABA "Tables" a miniatura e legenda de uma tabela
-            do idioma selecionado
-        -->
-        <div class="row table">
-            <!-- miniatura -->
-            <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
-            <!-- legenda -->
-            <xsl:apply-templates select="table-wrap[@xml:lang=$TEXT_LANG]" mode="tab-content-label-and-caption"></xsl:apply-templates>
-        </div>
-    </xsl:template>
+            Para table-wrap-group e table-wrap, cria no conteúdo da ABA "Tables":
+            - a miniatura
 
-    <xsl:template match="table-wrap[not(@xml:lang)]" mode="tab-content">
-        <!--
-            cria no conteúdo da ABA "Tables" a miniatura e legenda de uma tabela
-            que não depende do idioma
+            Para table-wrap-group:
+            - legendas de uma tabela em mais de 1 idioma
+            Para table-wrap:
+            - legenda de uma tabela em 1 idioma
         -->
         <div class="row table">
             <!-- miniatura -->
@@ -420,6 +415,13 @@
         </div>
     </xsl:template>
 
+    <xsl:template match="table-wrap-group" mode="tab-content-label-and-caption">
+        <!--
+            cria no conteúdo da ABA "Tables" a legenda de uma tabela
+        -->
+        <xsl:apply-templates select="table-wrap" mode="tab-content-label-and-caption"/>
+    </xsl:template>
+
     <xsl:template match="table-wrap" mode="tab-content-label-and-caption">
         <!--
             cria no conteúdo da ABA "Tables" a legenda de uma tabela

From cdc4e3682025f4899858afd332556d04695c9394 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 17:41:38 -0300
Subject: [PATCH 04/17] =?UTF-8?q?Refatora:=20apaga=20templates,=20move=20s?=
 =?UTF-8?q?eu=20conte=C3=BAdo=20para=20o=20bloco=20que=20o=20aplicava=20o?=
 =?UTF-8?q?=20template?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 128 +++++++-----------
 1 file changed, 50 insertions(+), 78 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index a4132a0ff..2b1d4f81d 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -325,46 +325,33 @@
         -->
         <div class="row fig">
             <!-- miniatura -->
-            <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
+            <xsl:variable name="location">
+                <xsl:apply-templates select="alternatives | graphic" mode="file-location-thumb"/>
+            </xsl:variable>
+            <div class="col-md-4">
+                <a data-toggle="modal" data-target="#ModalFig{@id}">
+                    <div>
+                        <xsl:choose>
+                            <xsl:when test="$location != ''">
+                                <xsl:attribute name="class">thumbImg</xsl:attribute>
+                                <img>
+                                    <xsl:attribute name="src"><xsl:value-of select="$location"/></xsl:attribute>
+                                </img>
+                            </xsl:when>
+                            <xsl:otherwise>
+                                <xsl:attribute name="class">thumbOff</xsl:attribute>
+                            </xsl:otherwise>
+                        </xsl:choose>
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
             <!-- legenda(s) -->
             <xsl:apply-templates select="." mode="tab-content-label-and-caption"></xsl:apply-templates>
         </div>
     </xsl:template>
 
-    <xsl:template match="fig | fig-group" mode="tab-content-thumbnail">
-        <!--
-            cria a miniatura de uma figura no conteúdo da ABA "Figures"
-        -->
-        <xsl:variable name="figid">
-            <xsl:choose>
-                <xsl:when test="@id"><xsl:value-of select="@id"/></xsl:when>
-                <xsl:otherwise></xsl:otherwise>
-            </xsl:choose>
-        </xsl:variable>
-        <xsl:variable name="location">
-            <xsl:apply-templates select="alternatives | graphic" mode="file-location-thumb"/>
-        </xsl:variable>
-        <div class="col-md-4">
-            <a data-toggle="modal" data-target="#ModalFig{$figid}">
-                <div>
-                    <xsl:choose>
-                        <xsl:when test="$location != ''">
-                            <xsl:attribute name="class">thumbImg</xsl:attribute>
-                            <img>
-                                <xsl:attribute name="src"><xsl:value-of select="$location"/></xsl:attribute>
-                            </img>
-                        </xsl:when>
-                        <xsl:otherwise>
-                            <xsl:attribute name="class">thumbOff</xsl:attribute>
-                        </xsl:otherwise>
-                    </xsl:choose>
-                    Thumbnail
-                    <div class="zoom"><span class="sci-ico-zoom"></span></div>
-                </div>
-            </a>
-        </div>
-    </xsl:template>
-
     <xsl:template match="fig-group" mode="tab-content-label-and-caption">
         <!--
             cria as legendas de uma figura no conteúdo da ABA "Figures"
@@ -393,28 +380,19 @@
         -->
         <div class="row table">
             <!-- miniatura -->
-            <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
+            <div class="col-md-4">
+                <a data-toggle="modal" data-target="#ModalTable{@id}">
+                    <div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
             <!-- legenda -->
             <xsl:apply-templates select="." mode="tab-content-label-and-caption"></xsl:apply-templates>
         </div>
     </xsl:template>
 
-    <xsl:template match="table-wrap | table-wrap-group" mode="tab-content-thumbnail">
-        <!--
-            cria no conteúdo da ABA "Tables" a miniatura de uma tabela
-            que não depende do idioma
-        -->
-        <xsl:variable name="location"><xsl:apply-templates select="." mode="file-location"/></xsl:variable>
-        <div class="col-md-4">
-            <a data-toggle="modal" data-target="#ModalTable{@id}">
-                <div class="thumbOff">
-                    Thumbnail
-                    <div class="zoom"><span class="sci-ico-zoom"></span></div>
-                </div>
-            </a>
-        </div>
-    </xsl:template>
-
     <xsl:template match="table-wrap-group" mode="tab-content-label-and-caption">
         <!--
             cria no conteúdo da ABA "Tables" a legenda de uma tabela
@@ -437,37 +415,31 @@
         -->
         <div class="row fig">
             <!-- miniatura -->
-            <xsl:apply-templates select="." mode="tab-content-thumbnail"></xsl:apply-templates>
+            <xsl:variable name="location"><xsl:apply-templates select="." mode="file-location"/></xsl:variable>
+            <div class="col-md-4">
+                <a data-toggle="modal" data-target="#ModalScheme{@id}">
+                    <div>
+                        <xsl:choose>
+                            <xsl:when test="graphic">
+                                <xsl:attribute name="class">thumbImg</xsl:attribute>
+                                <img>
+                                    <xsl:attribute name="src"><xsl:value-of select="$location"/></xsl:attribute>
+                                </img>
+                            </xsl:when>
+                            <xsl:otherwise>
+                                <xsl:attribute name="class">thumbOff</xsl:attribute>
+                            </xsl:otherwise>
+                        </xsl:choose>
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
             <!-- legenda -->
             <xsl:apply-templates select="." mode="tab-content-label-and-caption"></xsl:apply-templates>
         </div>
     </xsl:template>
 
-    <xsl:template match="disp-formula[@id]" mode="tab-content-thumbnail">
-        <!--
-            cria no conteúdo da ABA "Schemes" a miniatura de uma fórmula
-        -->
-        <xsl:variable name="location"><xsl:apply-templates select="." mode="file-location"/></xsl:variable>
-        <div class="col-md-4">
-            <a data-toggle="modal" data-target="#ModalScheme{@id}">
-                <div>
-                    <xsl:choose>
-                        <xsl:when test="graphic">
-                            <img>
-                                <xsl:attribute name="src"><xsl:value-of select="$location"/></xsl:attribute>
-                            </img>
-                        </xsl:when>
-                        <xsl:otherwise>
-                            <xsl:attribute name="class">thumbOff</xsl:attribute>
-                        </xsl:otherwise>
-                    </xsl:choose>
-                    Thumbnail
-                    <div class="zoom"><span class="sci-ico-zoom"></span></div>
-                </div>
-            </a>
-        </div>
-    </xsl:template>
-
     <xsl:template match="disp-formula[@id]" mode="tab-content-label-and-caption">
         <!--
             cria no conteúdo da ABA "Schemes" a legenda de uma fórmula

From aa9fd4b2c67a45c17dfc3ec5393d54628b6a1420 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 18:00:16 -0300
Subject: [PATCH 05/17] Reduz templates parecidos

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 26 +++++--------------
 1 file changed, 6 insertions(+), 20 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 2b1d4f81d..a64689e57 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -352,16 +352,18 @@
         </div>
     </xsl:template>
 
-    <xsl:template match="fig-group" mode="tab-content-label-and-caption">
+    <xsl:template match="fig-group | table-wrap-group" mode="tab-content-label-and-caption">
         <!--
             cria as legendas de uma figura no conteúdo da ABA "Figures"
+            cria no conteúdo da ABA "Tables" as legendas de uma tabela
         -->
-        <xsl:apply-templates select="fig" mode="tab-content-label-and-caption"/>
+        <xsl:apply-templates select="fig | table-wrap" mode="tab-content-label-and-caption"/>
     </xsl:template>
 
-    <xsl:template match="fig" mode="tab-content-label-and-caption">
+    <xsl:template match="fig | table-wrap" mode="tab-content-label-and-caption">
         <!--
-            cria a legenda de uma figura no conteúdo da ABA "Figures"
+            Cria a legenda de uma figura no conteúdo da ABA "Figures" ou
+            Cria a legenda de uma tabela no conteúdo da ABA "Tables"
         -->
         <div class="col-md-8">
             <xsl:apply-templates select="." mode="label-caption-thumb"></xsl:apply-templates>
@@ -393,22 +395,6 @@
         </div>
     </xsl:template>
 
-    <xsl:template match="table-wrap-group" mode="tab-content-label-and-caption">
-        <!--
-            cria no conteúdo da ABA "Tables" a legenda de uma tabela
-        -->
-        <xsl:apply-templates select="table-wrap" mode="tab-content-label-and-caption"/>
-    </xsl:template>
-
-    <xsl:template match="table-wrap" mode="tab-content-label-and-caption">
-        <!--
-            cria no conteúdo da ABA "Tables" a legenda de uma tabela
-        -->
-        <div class="col-md-8">
-            <xsl:apply-templates select="." mode="label-caption-thumb"></xsl:apply-templates>
-        </div>
-    </xsl:template>
-
     <xsl:template match="disp-formula[@id]" mode="tab-content">
         <!--
             cria no conteúdo da ABA "Scheme" a miniatura e legenda de uma fórmula

From 8c6d7e4ac8a7d25dc0e8b9e6f3a2249814afb5d7 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 18:15:03 -0300
Subject: [PATCH 06/17] =?UTF-8?q?Reduz=20a=20quantidade=20de=20templates,?=
 =?UTF-8?q?=20testa=20a=20exist=C3=AAncia=20de=20tradu=C3=A7=C3=A3o=20no?=
 =?UTF-8?q?=20template=20"principal"?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 82 +++----------------
 1 file changed, 13 insertions(+), 69 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index a64689e57..444eb729a 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -5,92 +5,36 @@
         <!--
             Cria todos os modals do documento
         -->
+        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+
         <!-- modal do contribs -->
         <xsl:apply-templates select="." mode="modal-contribs"/>
 
         <!-- modal que apresenta juntos figuras, tabelas e fórmulas -->
         <xsl:apply-templates select="." mode="modal-grouped-figs-tables-schemes"/>
 
-        <!-- cria um modal para cada figura -->
-        <xsl:apply-templates select="." mode="fig-individual-modal"/>
-
-        <!-- cria um modal para cada tabela -->
-        <xsl:apply-templates select="." mode="table-individual-modal"/>
-
-        <!-- cria um modal para cada fórmula -->
-        <xsl:apply-templates select="." mode="scheme-individual-modal"/>
-
-        <!-- cria um modal para como citar -->
-        <xsl:apply-templates select="." mode="modal-how2cite"/>
-    </xsl:template>
-
-    <xsl:template match="article" mode="table-individual-modal">
-        <!--
-            Cria um modal para cada tabela
-            encontrada em article,
-            de acordo com o idioma selecionado para o texto
-        -->
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+        <!-- cria um modal para cada figura, tabela e fórmula existente no body-->
+        <xsl:apply-templates select="front" mode="individual-modal"/>
 
         <xsl:choose>
             <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="table-individual-modal"/>
+                <xsl:apply-templates select="$translation" mode="individual-modal"/>
             </xsl:when>
             <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="table-individual-modal"/>
+                <xsl:apply-templates select="body" mode="individual-modal"/>
             </xsl:otherwise>
         </xsl:choose>
-    </xsl:template>
-
-    <xsl:template match="front | body | back | sub-article" mode="table-individual-modal">
-        <!-- cria um modal para cada tabela existente no body-->
-        <xsl:apply-templates select=".//table-wrap[@id] | .//table-wrap-group[@id]" mode="modal"/>
-    </xsl:template>
+        <xsl:apply-templates select="back" mode="individual-modal"/>
 
-    <xsl:template match="article" mode="scheme-individual-modal">
-        <!--
-            Cria um modal para cada fórmula
-            encontrada em article,
-            de acordo com o idioma selecionado para o texto
-        -->
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
-
-        <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="scheme-individual-modal"/>
-            </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="scheme-individual-modal"/>
-            </xsl:otherwise>
-        </xsl:choose>
-    </xsl:template>
-
-    <xsl:template match="front | body | back | sub-article" mode="scheme-individual-modal">
-        <!-- cria um modal para cada formula existente no body-->
-        <xsl:apply-templates select=".//disp-formula[@id]" mode="modal"/>
-    </xsl:template>
-
-    <xsl:template match="article" mode="fig-individual-modal">
-        <!--
-            Cria um modal para cada figura
-            encontrada em article,
-            de acordo com o idioma selecionado para o texto
-        -->
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
-
-        <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="fig-individual-modal"/>
-            </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="fig-individual-modal"/>
-            </xsl:otherwise>
-        </xsl:choose>
+        <!-- cria um modal para como citar -->
+        <xsl:apply-templates select="." mode="modal-how2cite"/>
     </xsl:template>
 
-    <xsl:template match="front | body | back | sub-article" mode="fig-individual-modal">
-        <!-- cria um modal para cada figura existente no body-->
+    <xsl:template match="front | body | back | sub-article" mode="individual-modal">
+        <!-- cria um modal para cada figura, tabela e fórmula existente no body-->
         <xsl:apply-templates select=".//*[fig]" mode="fig-modal"></xsl:apply-templates>
+        <xsl:apply-templates select=".//table-wrap[@id] | .//table-wrap-group[@id]" mode="modal"/>
+        <xsl:apply-templates select=".//disp-formula[@id]" mode="modal"/>
     </xsl:template>
 
     <xsl:template match="article" mode="modal-grouped-figs-tables-schemes">

From 99e9b327a6e7ecb09455f84c49e35fac3510f59d Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 19:08:18 -0300
Subject: [PATCH 07/17] =?UTF-8?q?Cria=20templates=20mais=20gen=C3=A9ricos?=
 =?UTF-8?q?=20para=20montar=20o=20conte=C3=BAdo=20das=20abas:=20figures,?=
 =?UTF-8?q?=20tables=20e=20schmes?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 107 +++++-------------
 1 file changed, 29 insertions(+), 78 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 444eb729a..802376e57 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -120,7 +120,9 @@
                                         cria o conteúdo da aba com rótulo "Figures"
                                     -->
                                      <div role="tabpanel" class="tab-pane active" id="figures">
-                                         <xsl:apply-templates select="." mode="figs-tab-content"/>
+                                         <xsl:apply-templates select="." mode="generic-tab-content">
+                                            <xsl:with-param name="tab_content_type">figures</xsl:with-param>
+                                         </xsl:apply-templates>
                                      </div>
                                  </xsl:if>
                                  <xsl:if test="number($total_tables) &gt; 0">
@@ -131,7 +133,9 @@
                                          <xsl:attribute name="class">tab-pane <xsl:if test="number($total_figs) = 0"> active</xsl:if></xsl:attribute>
                                          <xsl:attribute name="id">tables</xsl:attribute>
 
-                                         <xsl:apply-templates select="." mode="tables-tab-content"/>
+                                         <xsl:apply-templates select="." mode="generic-tab-content">
+                                            <xsl:with-param name="tab_content_type">tables</xsl:with-param>
+                                         </xsl:apply-templates>
                                      </div>
                                  </xsl:if>
                                  <xsl:if test="number($total_formulas) &gt; 0">
@@ -142,7 +146,9 @@
                                          <xsl:attribute name="class">tab-pane <xsl:if test="number($total_figs) + number($total_tables) = 0"> active</xsl:if></xsl:attribute>
                                          <xsl:attribute name="id">schemes</xsl:attribute>
 
-                                         <xsl:apply-templates select="." mode="schemes-tab-content"/>
+                                         <xsl:apply-templates select="." mode="generic-tab-content">
+                                            <xsl:with-param name="tab_content_type">schemes</xsl:with-param>
+                                         </xsl:apply-templates>
                                      </div>
                                  </xsl:if>
                              </div>
@@ -153,65 +159,44 @@
          </xsl:if>
     </xsl:template>
 
-    <xsl:template match="article" mode="figs-tab-content">
-        <!--
-        Conteúdo da aba "Figures", selecionando todas as figuras relacionadas
-        com o idioma do texto selecionado
-        -->
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+    <xsl:template match="article" mode="generic-tab-content">
+        <xsl:param name="tab_content_type"/>
 
-        <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="figs-tab-content"/>
-            </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="figs-tab-content"/>
-            </xsl:otherwise>
-        </xsl:choose>
-    </xsl:template>
-
-    <xsl:template match="article" mode="tables-tab-content">
-        <!--
-        Conteúdo da aba "Tables", selecionando todas as tabelas relacionadas
-        com o idioma do texto selecionado
-        -->
         <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
 
         <xsl:choose>
             <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="tables-tab-content"/>
+                <xsl:apply-templates select="front | $translation | back" mode="generic-tab-content">
+                    <xsl:with-param name="tab_content_type" select="$tab_content_type"/>
+                </xsl:apply-templates>
             </xsl:when>
             <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="tables-tab-content"/>
+                <xsl:apply-templates select="front | body | back" mode="generic-tab-content">
+                    <xsl:with-param name="tab_content_type" select="$tab_content_type"/>
+                </xsl:apply-templates>
             </xsl:otherwise>
         </xsl:choose>
     </xsl:template>
 
-    <xsl:template match="article" mode="schemes-tab-content">
+    <xsl:template match="sub-article | front | body | back" mode="generic-tab-content">
+        <xsl:param name="tab_content_type"/>
         <!--
-        Conteúdo da aba "Schemes", selecionando todas as fórmulas relacionadas
-        com o idioma do texto selecionado
+        Seleciona os elementos que contém "fig",
+        para criar o conteúdo de cada fig no Modal na aba "Figures"
         -->
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
-
         <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="schemes-tab-content"/>
+            <xsl:when test="$tab_content_type='figures'">
+                <xsl:apply-templates select=".//*[fig]" mode="figs-tab-content"/>
+            </xsl:when>
+            <xsl:when test="$tab_content_type='tables'">
+                <xsl:apply-templates select=".//table-wrap-group[table-wrap] | .//*[table-wrap and name()!='table-wrap-group']/table-wrap" mode="tab-content"/>
+            </xsl:when>
+            <xsl:when test="$tab_content_type='schemes'">
+                <xsl:apply-templates select=".//disp-formula[@id]" mode="tab-content"/>
             </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="schemes-tab-content"/>
-            </xsl:otherwise>
         </xsl:choose>
     </xsl:template>
 
-    <xsl:template match="sub-article | front | body | back" mode="figs-tab-content">
-        <!--
-        Seleciona os elementos que contém "fig",
-        para criar o conteúdo de cada fig no Modal na aba "Figures"
-        -->
-        <xsl:apply-templates select=".//*[fig]" mode="figs-tab-content"/>
-    </xsl:template>
-
     <xsl:template match="*[fig]" mode="fig-modal">
         <!--
         cria o conteúdo de uma figura no Modal na aba "Figures"
@@ -240,22 +225,6 @@
         </xsl:choose>
     </xsl:template>
 
-    <xsl:template match="sub-article | front | body | back" mode="tables-tab-content">
-        <!--
-        Seleciona os elementos de tabela para
-        criar o conteúdo de cada tabela no Modal na aba "Tables"
-        -->
-        <xsl:apply-templates select=".//table-wrap-group[table-wrap] | .//*[table-wrap and name()!='table-wrap-group']/table-wrap" mode="tab-content"/>
-    </xsl:template>
-
-    <xsl:template match="sub-article | front | body | back" mode="schemes-tab-content">
-        <!--
-        Seleciona os elementos disp-formula para
-        criar o conteúdo de cada fórmula no Modal na aba "Schemes"
-        -->
-        <xsl:apply-templates select=".//disp-formula[@id]" mode="tab-content"/>
-    </xsl:template>
-
     <xsl:template match="fig-group[@id] | fig" mode="tab-content">
         <!--
             Para fig-group e fig, cria no conteúdo da ABA "Figures":
@@ -415,24 +384,6 @@
         <xsl:value-of select="number($f)+number($b)+number($bk)"/>
     </xsl:template>
 
-    <xsl:template match="article" mode="get-total-formulas">
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
-
-        <xsl:variable name="f"><xsl:apply-templates select="front" mode="get-total-formulas"/></xsl:variable>
-        <xsl:variable name="bk"><xsl:apply-templates select="back" mode="get-total-formulas"/></xsl:variable>
-        <xsl:variable name="b">
-        <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="$translation" mode="get-total-formulas"/>
-            </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="body" mode="get-total-formulas"/>
-            </xsl:otherwise>
-        </xsl:choose>
-        </xsl:variable>
-        <xsl:value-of select="number($f)+number($b)+number($bk)"/>
-    </xsl:template>
-
     <xsl:template match="sub-article | front | body | back" mode="get-total-figs">
         <xsl:value-of select="count(.//fig-group[@id]/fig[@xml:lang][1]) + count(.//fig[not(@xml:lang)])"/>
     </xsl:template>

From 4f61f9252af393e775b31c21f20b5246a765b039 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 19:21:05 -0300
Subject: [PATCH 08/17] Generaliza os templates que somam os elementos tables,
 figures e schemes

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 72 ++++++++++---------
 1 file changed, 39 insertions(+), 33 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 802376e57..663c90900 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -44,13 +44,19 @@
         -->
         <!-- FIXME -->
         <xsl:variable name="total_figs">
-            <xsl:apply-templates select="." mode="get-total-figs"/>
+            <xsl:apply-templates select="." mode="get-total">
+                <xsl:with-param name="content_type">figures</xsl:with-param>
+            </xsl:apply-templates>
         </xsl:variable>
         <xsl:variable name="total_tables">
-            <xsl:apply-templates select="." mode="get-total-tables"/>
+            <xsl:apply-templates select="." mode="get-total">
+                <xsl:with-param name="content_type">tables</xsl:with-param>
+            </xsl:apply-templates>
         </xsl:variable>
         <xsl:variable name="total_formulas">
-            <xsl:apply-templates select="." mode="get-total-formulas"/>
+            <xsl:apply-templates select="." mode="get-total">
+                <xsl:with-param name="content_type">schemes</xsl:with-param>
+            </xsl:apply-templates>
         </xsl:variable>
 
         <xsl:if test="number($total_figs) + number($total_tables) + number($total_formulas) &gt; 0">
@@ -348,51 +354,51 @@
         </div>
     </xsl:template>
 
-    <xsl:template match="article" mode="get-total-figs">
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+    <xsl:template match="article" mode="get-total">
+        <xsl:param name="content_type"/>
 
-        <xsl:variable name="f"><xsl:apply-templates select="front" mode="get-total-figs"/></xsl:variable>
-        <xsl:variable name="bk"><xsl:apply-templates select="back" mode="get-total-figs"/></xsl:variable>
+        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+        <xsl:variable name="f">
+            <xsl:apply-templates select="front" mode="get-total">
+                <xsl:with-param name="content_type" select="$content_type"/>
+            </xsl:apply-templates>
+        </xsl:variable>
+        <xsl:variable name="bk">
+            <xsl:apply-templates select="back" mode="get-total">
+                <xsl:with-param name="content_type" select="$content_type"/>
+            </xsl:apply-templates>
+        </xsl:variable>
         <xsl:variable name="b">
         <xsl:choose>
             <xsl:when test="$translation">
-                <xsl:apply-templates select="$translation" mode="get-total-figs"/>
+                <xsl:apply-templates select="$translation" mode="get-total">
+                    <xsl:with-param name="content_type" select="$content_type"/>
+                </xsl:apply-templates>
             </xsl:when>
             <xsl:otherwise>
-                <xsl:apply-templates select="body" mode="get-total-figs"/>
+                <xsl:apply-templates select="body" mode="get-total">
+                    <xsl:with-param name="content_type" select="$content_type"/>
+                </xsl:apply-templates>
             </xsl:otherwise>
         </xsl:choose>
         </xsl:variable>
         <xsl:value-of select="number($f)+number($b)+number($bk)"/>
     </xsl:template>
 
-    <xsl:template match="article" mode="get-total-tables">
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+    <xsl:template match="sub-article | front | body | back" mode="get-total">
+        <xsl:param name="content_type"/>
 
-        <xsl:variable name="f"><xsl:apply-templates select="front" mode="get-total-tables"/></xsl:variable>
-        <xsl:variable name="bk"><xsl:apply-templates select="back" mode="get-total-tables"/></xsl:variable>
-        <xsl:variable name="b">
         <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="$translation" mode="get-total-tables"/>
+            <xsl:when test="$content_type='figures'">
+                <xsl:value-of select="count(.//fig-group[@id]/fig[@xml:lang][1]) + count(.//fig[not(@xml:lang)])"/>
             </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="body" mode="get-total-tables"/>
-            </xsl:otherwise>
-        </xsl:choose>
-        </xsl:variable>
-        <xsl:value-of select="number($f)+number($b)+number($bk)"/>
-    </xsl:template>
-
-    <xsl:template match="sub-article | front | body | back" mode="get-total-figs">
-        <xsl:value-of select="count(.//fig-group[@id]/fig[@xml:lang][1]) + count(.//fig[not(@xml:lang)])"/>
-    </xsl:template>
-
-    <xsl:template match="sub-article | front | body | back" mode="get-total-tables">
-        <xsl:value-of select="count(.//table-wrap-group) + count(.//*[table-wrap and name()!='table-wrap-group']//table-wrap)"/>
+            <xsl:when test="$content_type='tables'">
+                <xsl:value-of select="count(.//table-wrap-group) + count(.//*[table-wrap and name()!='table-wrap-group']//table-wrap)"/>
+            </xsl:when>
+            <xsl:when test="$content_type='schemes'">
+                <xsl:value-of select="count(.//disp-formula[@id])"/>
+            </xsl:when>
+        </xsl:choose>        
     </xsl:template>
 
-    <xsl:template match="sub-article | front | body | back" mode="get-total-formulas">
-        <xsl:value-of select="count(.//disp-formula[@id])"/>
-    </xsl:template>
 </xsl:stylesheet>
\ No newline at end of file

From 292ee551275dbd7c38b7fc810f8925e4e59ce86f Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 19:57:42 -0300
Subject: [PATCH 09/17] =?UTF-8?q?Cria=20um=20template=20gen=C3=A9rico=20pa?=
 =?UTF-8?q?ra=20apresentar=20=20os=20r=C3=B3tulos=20das=20abas?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 84 +++++++++----------
 1 file changed, 42 insertions(+), 42 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 663c90900..5a254b623 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -76,48 +76,26 @@
                          </div>
                          <div class="modal-body">
                              <ul class="nav nav-tabs md-tabs" role="tablist">
-                                <xsl:if test="number($total_figs) &gt; 0">
-                                    <!--
-                                        cria aba com rótulo "Figures" e quantidade de figuras
-                                    -->
-                                    <li role="presentation" class="col-md-4 col-sm-4 active">
-                                         <a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">
-                                             <xsl:apply-templates select="." mode="interface">
-                                                 <xsl:with-param name="text">Figures</xsl:with-param>
-                                             </xsl:apply-templates>
-                                             (<xsl:value-of select="$total_figs"/>)
-                                         </a>
-                                     </li>
-                                 </xsl:if>
-                                 <xsl:if test="number($total_tables) &gt; 0">
-                                     <!--
-                                        cria aba com rótulo "Tables" e quantidade de tabelas
-                                    -->
-                                     <li role="presentation">
-                                         <xsl:attribute name="class">col-md-4 col-sm-4 <xsl:if test="number($total_figs) = 0"> active</xsl:if></xsl:attribute>
-                                         <a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">
-                                             <xsl:apply-templates select="." mode="interface">
-                                                 <xsl:with-param name="text">Tables</xsl:with-param>
-                                             </xsl:apply-templates>
-                                             (<xsl:value-of select="$total_tables"/>)
-                                         </a>
-                                     </li>
-                                 </xsl:if>
-                                 <xsl:if test="number($total_formulas) &gt; 0">
-                                     <!--
-                                        cria aba com rótulo "Scheme" e quantidade de fórmulas
-                                    -->
-                                     <li role="presentation">
-                                         <xsl:attribute name="class">col-md-4 col-sm-4<xsl:if test="number($total_figs) + number($total_tables) = 0"> active</xsl:if></xsl:attribute>
-
-                                         <a href="#schemes" aria-controls="schemes" role="tab" data-toggle="tab">
-                                             <xsl:apply-templates select="." mode="interface">
-                                                 <xsl:with-param name="text">Formulas</xsl:with-param>
-                                             </xsl:apply-templates>
-                                             (<xsl:value-of select="$total_formulas"/>)
-                                         </a>
-                                     </li>
-                                 </xsl:if>
+                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                    <xsl:with-param name="previous_tab_total">0</xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_figs"/>
+                                    <xsl:with-param name="title">Figures</xsl:with-param>
+                                    <xsl:with-param name="content_type">figures</xsl:with-param>
+                                </xsl:apply-templates>
+
+                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                    <xsl:with-param name="previous_tab_total"><xsl:value-of select="$total_figs"/></xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_tables"/>
+                                    <xsl:with-param name="title">Tables</xsl:with-param>
+                                    <xsl:with-param name="content_type">tables</xsl:with-param>
+                                </xsl:apply-templates>
+
+                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                    <xsl:with-param name="previous_tab_total"><xsl:value-of select="number($total_figs)+number($total_formulas)"/></xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_formulas"/>
+                                    <xsl:with-param name="title">Formulas</xsl:with-param>
+                                    <xsl:with-param name="content_type">schemes</xsl:with-param>
+                                </xsl:apply-templates>
                              </ul>
                              <div class="clearfix"></div>
                              <div class="tab-content">
@@ -165,6 +143,28 @@
          </xsl:if>
     </xsl:template>
 
+    <xsl:template match="article" mode="generic-tab-content-title-and-total">
+        <xsl:param name="previous_tab_total">0</xsl:param>
+        <xsl:param name="total"/>
+        <xsl:param name="title"/>
+        <xsl:param name="content_type"/>
+
+        <xsl:if test="number($total) &gt; 0">
+            <!--
+                cria aba com rótulo "$title ($total)" 
+            -->
+            <li role="presentation">
+                <xsl:attribute name="class">col-md-4 col-sm-4 <xsl:if test="number($previous_tab_total) = 0"> active</xsl:if></xsl:attribute>
+                <a href="#{$content_type}" aria-controls="{$content_type}" role="tab" data-toggle="tab">
+                    <xsl:apply-templates select="." mode="interface">
+                        <xsl:with-param name="text" select="$title"/>
+                    </xsl:apply-templates>
+                    (<xsl:value-of select="$total"/>)
+                </a>
+            </li>
+        </xsl:if>
+    </xsl:template>
+
     <xsl:template match="article" mode="generic-tab-content">
         <xsl:param name="tab_content_type"/>
 

From a0439a14014f9e72c60d4d14bc48387d06dc1e74 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 20:37:23 -0300
Subject: [PATCH 10/17] =?UTF-8?q?Cria=20um=20template=20gen=C3=A9rico=20pa?=
 =?UTF-8?q?ra=20apresentar=20o=20conte=C3=BAdo=20das=20abas?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        | 107 +++++++++---------
 1 file changed, 51 insertions(+), 56 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 5a254b623..2b48cdd02 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -76,21 +76,21 @@
                          </div>
                          <div class="modal-body">
                              <ul class="nav nav-tabs md-tabs" role="tablist">
-                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                <xsl:apply-templates select="." mode="generic-tab-title-and-total">
                                     <xsl:with-param name="previous_tab_total">0</xsl:with-param>
                                     <xsl:with-param name="total" select="$total_figs"/>
                                     <xsl:with-param name="title">Figures</xsl:with-param>
                                     <xsl:with-param name="content_type">figures</xsl:with-param>
                                 </xsl:apply-templates>
 
-                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                <xsl:apply-templates select="." mode="generic-tab-title-and-total">
                                     <xsl:with-param name="previous_tab_total"><xsl:value-of select="$total_figs"/></xsl:with-param>
                                     <xsl:with-param name="total" select="$total_tables"/>
                                     <xsl:with-param name="title">Tables</xsl:with-param>
                                     <xsl:with-param name="content_type">tables</xsl:with-param>
                                 </xsl:apply-templates>
 
-                                <xsl:apply-templates select="." mode="generic-tab-content-title-and-total">
+                                <xsl:apply-templates select="." mode="generic-tab-title-and-total">
                                     <xsl:with-param name="previous_tab_total"><xsl:value-of select="number($total_figs)+number($total_formulas)"/></xsl:with-param>
                                     <xsl:with-param name="total" select="$total_formulas"/>
                                     <xsl:with-param name="title">Formulas</xsl:with-param>
@@ -99,42 +99,23 @@
                              </ul>
                              <div class="clearfix"></div>
                              <div class="tab-content">
-                                 <xsl:if test="number($total_figs) &gt; 0">
-                                    <!--
-                                        cria o conteúdo da aba com rótulo "Figures"
-                                    -->
-                                     <div role="tabpanel" class="tab-pane active" id="figures">
-                                         <xsl:apply-templates select="." mode="generic-tab-content">
-                                            <xsl:with-param name="tab_content_type">figures</xsl:with-param>
-                                         </xsl:apply-templates>
-                                     </div>
-                                 </xsl:if>
-                                 <xsl:if test="number($total_tables) &gt; 0">
-                                    <!--
-                                        cria o conteúdo da aba com rótulo "Tables"
-                                    -->
-                                     <div role="tabpanel">
-                                         <xsl:attribute name="class">tab-pane <xsl:if test="number($total_figs) = 0"> active</xsl:if></xsl:attribute>
-                                         <xsl:attribute name="id">tables</xsl:attribute>
-
-                                         <xsl:apply-templates select="." mode="generic-tab-content">
-                                            <xsl:with-param name="tab_content_type">tables</xsl:with-param>
-                                         </xsl:apply-templates>
-                                     </div>
-                                 </xsl:if>
-                                 <xsl:if test="number($total_formulas) &gt; 0">
-                                    <!--
-                                        cria o conteúdo da aba com rótulo "Formulas"
-                                    -->
-                                     <div role="tabpanel">
-                                         <xsl:attribute name="class">tab-pane <xsl:if test="number($total_figs) + number($total_tables) = 0"> active</xsl:if></xsl:attribute>
-                                         <xsl:attribute name="id">schemes</xsl:attribute>
-
-                                         <xsl:apply-templates select="." mode="generic-tab-content">
-                                            <xsl:with-param name="tab_content_type">schemes</xsl:with-param>
-                                         </xsl:apply-templates>
-                                     </div>
-                                 </xsl:if>
+                                <xsl:apply-templates select="." mode="generic-tab-panel">
+                                    <xsl:with-param name="previous_tab_total">0</xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_figs"/>
+                                    <xsl:with-param name="content_type">figures</xsl:with-param>
+                                </xsl:apply-templates>
+
+                                <xsl:apply-templates select="." mode="generic-tab-panel">
+                                    <xsl:with-param name="previous_tab_total"><xsl:value-of select="$total_figs"/></xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_tables"/>
+                                    <xsl:with-param name="content_type">tables</xsl:with-param>
+                                </xsl:apply-templates>
+
+                                <xsl:apply-templates select="." mode="generic-tab-panel">
+                                    <xsl:with-param name="previous_tab_total"><xsl:value-of select="number($total_figs)+number($total_formulas)"/></xsl:with-param>
+                                    <xsl:with-param name="total" select="$total_formulas"/>
+                                    <xsl:with-param name="content_type">schemes</xsl:with-param>
+                                </xsl:apply-templates>
                              </div>
                          </div>
                      </div>
@@ -143,7 +124,7 @@
          </xsl:if>
     </xsl:template>
 
-    <xsl:template match="article" mode="generic-tab-content-title-and-total">
+    <xsl:template match="article" mode="generic-tab-title-and-total">
         <xsl:param name="previous_tab_total">0</xsl:param>
         <xsl:param name="total"/>
         <xsl:param name="title"/>
@@ -154,7 +135,7 @@
                 cria aba com rótulo "$title ($total)" 
             -->
             <li role="presentation">
-                <xsl:attribute name="class">col-md-4 col-sm-4 <xsl:if test="number($previous_tab_total) = 0"> active</xsl:if></xsl:attribute>
+                <xsl:attribute name="class">col-md-4 col-sm-4 <xsl:if test="number($previous_tab_total) = 0">active</xsl:if></xsl:attribute>
                 <a href="#{$content_type}" aria-controls="{$content_type}" role="tab" data-toggle="tab">
                     <xsl:apply-templates select="." mode="interface">
                         <xsl:with-param name="text" select="$title"/>
@@ -165,23 +146,37 @@
         </xsl:if>
     </xsl:template>
 
-    <xsl:template match="article" mode="generic-tab-content">
-        <xsl:param name="tab_content_type"/>
+    <xsl:template match="article" mode="generic-tab-panel">
+        <xsl:param name="previous_tab_total">0</xsl:param>
+        <xsl:param name="total"/>
+        <xsl:param name="content_type"/>
 
-        <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+        <xsl:if test="number($total) &gt; 0">
+            <!--
+                cria o conteúdo da aba do rótulo "$title ($total)" 
+            -->
+            <div role="tabpanel">
+                <xsl:attribute name="class">tab-pane <xsl:if test="number($previous_tab_total) = 0">active</xsl:if></xsl:attribute>
+
+                <xsl:attribute name="id"><xsl:value-of select="$content_type"/></xsl:attribute>
+
+                <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
+
+                <xsl:choose>
+                    <xsl:when test="$translation">
+                        <xsl:apply-templates select="front | $translation | back" mode="generic-tab-content">
+                            <xsl:with-param name="tab_content_type" select="$content_type"/>
+                        </xsl:apply-templates>
+                    </xsl:when>
+                    <xsl:otherwise>
+                        <xsl:apply-templates select="front | body | back" mode="generic-tab-content">
+                            <xsl:with-param name="tab_content_type" select="$content_type"/>
+                        </xsl:apply-templates>
+                    </xsl:otherwise>
+                </xsl:choose>
 
-        <xsl:choose>
-            <xsl:when test="$translation">
-                <xsl:apply-templates select="front | $translation | back" mode="generic-tab-content">
-                    <xsl:with-param name="tab_content_type" select="$tab_content_type"/>
-                </xsl:apply-templates>
-            </xsl:when>
-            <xsl:otherwise>
-                <xsl:apply-templates select="front | body | back" mode="generic-tab-content">
-                    <xsl:with-param name="tab_content_type" select="$tab_content_type"/>
-                </xsl:apply-templates>
-            </xsl:otherwise>
-        </xsl:choose>
+            </div>
+        </xsl:if>
     </xsl:template>
 
     <xsl:template match="sub-article | front | body | back" mode="generic-tab-content">

From dc1ae7739aba18d4c823e1cddf78294a7aea4540 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Thu, 24 Feb 2022 20:43:07 -0300
Subject: [PATCH 11/17] =?UTF-8?q?Corrige=20coment=C3=A1rio?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl | 4 +---
 1 file changed, 1 insertion(+), 3 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index 2b48cdd02..a14e6058a 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -42,7 +42,6 @@
             Modal que apresenta juntos figuras, tabelas e fórmulas presentes
             em um dado idioma do texto do artigo
         -->
-        <!-- FIXME -->
         <xsl:variable name="total_figs">
             <xsl:apply-templates select="." mode="get-total">
                 <xsl:with-param name="content_type">figures</xsl:with-param>
@@ -182,8 +181,7 @@
     <xsl:template match="sub-article | front | body | back" mode="generic-tab-content">
         <xsl:param name="tab_content_type"/>
         <!--
-        Seleciona os elementos que contém "fig",
-        para criar o conteúdo de cada fig no Modal na aba "Figures"
+        Apresenta o conteúdo da aba
         -->
         <xsl:choose>
             <xsl:when test="$tab_content_type='figures'">

From e4a9421be062473feb82aa534037c47040b1c79b Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Fri, 25 Feb 2022 10:45:39 -0300
Subject: [PATCH 12/17] =?UTF-8?q?Remove=20`@id`=20para=20considerar=20que?=
 =?UTF-8?q?=20=C3=A9=20v=C3=A1lido=20haver=201=20figura=20sem=20`@id`?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl | 2 +-
 1 file changed, 1 insertion(+), 1 deletion(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl b/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
index a3105f988..309e267ba 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/article-text-fig.xsl
@@ -6,7 +6,7 @@
     exclude-result-prefixes="xlink mml"
     version="1.0">
 
-    <xsl:template match="fig[@id] | fig-group[@id]">
+    <xsl:template match="fig | fig-group[@id]">
         <!--
         Cria a miniatura no texto completo, que ao ser clicada mostra a figura
         ampliada

From 17bb8ea5374d74f1f3aaf6af3fb2a730af75ea6f Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Fri, 25 Feb 2022 19:55:41 -0300
Subject: [PATCH 13/17] =?UTF-8?q?Faz=20testes=20para=20apresenta=C3=A7?=
 =?UTF-8?q?=C3=A3o=20de=20figura=20sem=20`@id`=20e=20faz=20ajustes=20em=20?=
 =?UTF-8?q?XSL=20para=20tratar=20de=20tag=20`fig`=20presentes=20diretament?=
 =?UTF-8?q?e=20em=20`body`?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 .../htmlgenerator/v2.0/html-modals.xsl        |  48 ++--
 tests/test_htmlgenerator.py                   | 219 ++++++++++++++++++
 2 files changed, 252 insertions(+), 15 deletions(-)

diff --git a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
index a14e6058a..dbf7a3cc0 100644
--- a/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
+++ b/packtools/catalogs/htmlgenerator/v2.0/html-modals.xsl
@@ -32,7 +32,7 @@
 
     <xsl:template match="front | body | back | sub-article" mode="individual-modal">
         <!-- cria um modal para cada figura, tabela e fórmula existente no body-->
-        <xsl:apply-templates select=".//*[fig]" mode="fig-modal"></xsl:apply-templates>
+        <xsl:apply-templates select=".//*[fig] | fig" mode="fig-modal"></xsl:apply-templates>
         <xsl:apply-templates select=".//table-wrap[@id] | .//table-wrap-group[@id]" mode="modal"/>
         <xsl:apply-templates select=".//disp-formula[@id]" mode="modal"/>
     </xsl:template>
@@ -57,7 +57,6 @@
                 <xsl:with-param name="content_type">schemes</xsl:with-param>
             </xsl:apply-templates>
         </xsl:variable>
-
         <xsl:if test="number($total_figs) + number($total_tables) + number($total_formulas) &gt; 0">
              <div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true">
                  <div class="modal-dialog">
@@ -185,10 +184,10 @@
         -->
         <xsl:choose>
             <xsl:when test="$tab_content_type='figures'">
-                <xsl:apply-templates select=".//*[fig]" mode="figs-tab-content"/>
+                <xsl:apply-templates select="fig | .//*[fig]" mode="figs-tab-content"/>
             </xsl:when>
             <xsl:when test="$tab_content_type='tables'">
-                <xsl:apply-templates select=".//table-wrap-group[table-wrap] | .//*[table-wrap and name()!='table-wrap-group']/table-wrap" mode="tab-content"/>
+                <xsl:apply-templates select="table-wrap | .//table-wrap-group[table-wrap] | .//*[table-wrap and name()!='table-wrap-group']/table-wrap" mode="tab-content"/>
             </xsl:when>
             <xsl:when test="$tab_content_type='schemes'">
                 <xsl:apply-templates select=".//disp-formula[@id]" mode="tab-content"/>
@@ -196,6 +195,10 @@
         </xsl:choose>
     </xsl:template>
 
+    <xsl:template match="fig" mode="fig-modal">
+        <xsl:apply-templates select="." mode="modal"/>
+    </xsl:template>
+
     <xsl:template match="*[fig]" mode="fig-modal">
         <!--
         cria o conteúdo de uma figura no Modal na aba "Figures"
@@ -210,6 +213,10 @@
         </xsl:choose>
     </xsl:template>
 
+    <xsl:template match="fig" mode="figs-tab-content">
+        <xsl:apply-templates select="." mode="tab-content"/>
+    </xsl:template>
+
     <xsl:template match="*[fig]" mode="figs-tab-content">
         <!--
         cria o conteúdo de uma figura no Modal na aba "Figures"
@@ -352,27 +359,38 @@
 
         <xsl:variable name="translation" select=".//sub-article[@xml:lang=$TEXT_LANG and @article-type='translation']"/>
         <xsl:variable name="f">
-            <xsl:apply-templates select="front" mode="get-total">
-                <xsl:with-param name="content_type" select="$content_type"/>
-            </xsl:apply-templates>
+            <xsl:choose>
+                <xsl:when test="front">
+                    <xsl:apply-templates select="front" mode="get-total">
+                        <xsl:with-param name="content_type" select="$content_type"/>
+                    </xsl:apply-templates>
+                </xsl:when>
+                <xsl:otherwise>0</xsl:otherwise>
+            </xsl:choose>
         </xsl:variable>
         <xsl:variable name="bk">
-            <xsl:apply-templates select="back" mode="get-total">
-                <xsl:with-param name="content_type" select="$content_type"/>
-            </xsl:apply-templates>
+            <xsl:choose>
+                <xsl:when test="back">
+                    <xsl:apply-templates select="back" mode="get-total">
+                        <xsl:with-param name="content_type" select="$content_type"/>
+                    </xsl:apply-templates>
+                </xsl:when>
+                <xsl:otherwise>0</xsl:otherwise>
+            </xsl:choose>
         </xsl:variable>
         <xsl:variable name="b">
         <xsl:choose>
             <xsl:when test="$translation">
                 <xsl:apply-templates select="$translation" mode="get-total">
-                    <xsl:with-param name="content_type" select="$content_type"/>
+                    <xsl:with-param name="content_type"><xsl:value-of select="$content_type"/></xsl:with-param>
                 </xsl:apply-templates>
             </xsl:when>
-            <xsl:otherwise>
+            <xsl:when test="body">
                 <xsl:apply-templates select="body" mode="get-total">
                     <xsl:with-param name="content_type" select="$content_type"/>
                 </xsl:apply-templates>
-            </xsl:otherwise>
+            </xsl:when>
+            <xsl:otherwise>0</xsl:otherwise>
         </xsl:choose>
         </xsl:variable>
         <xsl:value-of select="number($f)+number($b)+number($bk)"/>
@@ -383,10 +401,10 @@
 
         <xsl:choose>
             <xsl:when test="$content_type='figures'">
-                <xsl:value-of select="count(.//fig-group[@id]/fig[@xml:lang][1]) + count(.//fig[not(@xml:lang)])"/>
+                <xsl:value-of select="count(fig)"/>
             </xsl:when>
             <xsl:when test="$content_type='tables'">
-                <xsl:value-of select="count(.//table-wrap-group) + count(.//*[table-wrap and name()!='table-wrap-group']//table-wrap)"/>
+                <xsl:value-of select="count(./table-wrap) + count(.//table-wrap-group) + count(.//*[table-wrap and name()!='table-wrap-group']//table-wrap)"/>
             </xsl:when>
             <xsl:when test="$content_type='schemes'">
                 <xsl:value-of select="count(.//disp-formula[@id])"/>
diff --git a/tests/test_htmlgenerator.py b/tests/test_htmlgenerator.py
index 48fdf25f1..02bf73cf8 100644
--- a/tests/test_htmlgenerator.py
+++ b/tests/test_htmlgenerator.py
@@ -9,6 +9,18 @@
 from packtools import domain
 
 
+NAMESPACES = {
+    "xlink": "http://www.w3.org/1999/xlink",
+}
+
+
+def _get_ns_attr(node, attr):
+    if node is not None:
+        ns, attr = attr.split(":")
+        ns = "{" + f'{NAMESPACES.get(ns)}' + "}"
+        return node.attrib.get(ns + attr)
+
+
 def setup_tmpfile(method):
     def wrapper(self):
         valid_tmpfile = NamedTemporaryFile()
@@ -1379,3 +1391,210 @@ def test_fig_group_thumbnail(self):
         self.assertIn("Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.", texts)
         self.assertIn("Figure 1", texts)
         self.assertIn("Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.", texts)
+
+
+class HTMLGeneratorFigWithoutIdTests(unittest.TestCase):
+
+    def setUp(self):
+        sample = u"""<article
+                      xmlns:mml="http://www.w3.org/1998/Math/MathML"
+                      xmlns:xlink="http://www.w3.org/1999/xlink"
+                      xml:lang="pt">
+                      <body>
+        <fig>
+            <label>Figura 1.</label>
+            <caption>
+                <title>Correlação entre o teor de fenóis totais e CE50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+            </caption>
+            <graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf1.jpg"/>
+            <attrib><xref ref-type="fig" rid="f1">Figure 1</xref>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+        </fig>
+        </body></article>
+        """
+        et = get_xml_tree_from_string(sample)
+        self.html = domain.HTMLGenerator.parse(et, valid_only=False).generate('pt')
+        # print(etree.tostring(self.html))
+
+    def test_fig_modal(self):
+        """
+        Test de modal
+        <div class="modal fade ModalFigs" id="ModalFig" tabindex="-1" role="dialog" aria-hidden="true">
+            <div class="modal-dialog modal-lg">
+            <div class="modal-content">
+                <div class="modal-header">
+                    <button type="button" class="close" data-dismiss="modal">
+                    <span aria-hidden="true">×</span><span class="sr-only">Close</span></button>
+                    <a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <span class="sci-ico-newWindow"></span>
+                    </a>
+                    <h4 class="modal-title">
+                        <span class="sci-ico-fileFigure"></span>Figura 1.   Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+                    </h4>
+                </div>
+                <div class="modal-body">
+                    <a href="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                    </a>
+                    <small>
+                        <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1">
+                            <span class="sci-ico-fileFigure"></span>Figure 1</a>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+                </div>
+            </div>
+            </div>
+        </div>
+        """
+        # div[@id='ModalFig'] (sem id)
+        div_modal_fig = self.html.find('.//div[@id="ModalFig"]')
+
+        # class="modal-header" has href with figure path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-header']/a").get("href")
+        )
+
+        # class="modal-title" has label and caption content
+        text = etree.tostring(
+            div_modal_fig.find('.//h4[@class="modal-title"]'),
+            encoding="utf-8"
+        ).decode("utf-8")
+
+        self.assertIn("Figura 1", text)
+        self.assertIn("Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", text)
+
+        # class="modal-body" has link to image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-body']/a").get("href")
+        )
+
+        # class="modal-body" has src with image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-body']/a/img").get("src")
+        )
+
+        # class="modal-body" has `attrib` text presented inner `<small/>`
+        small = div_modal_fig.find(".//div[@class='modal-body']/small")
+        self.assertIn(
+            "Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.",
+            etree.tostring(small, encoding="utf-8").decode("utf-8")
+        )
+
+    def test_fig_in_text__thumbnail_and_label(self):
+        """
+        Test the html expected to display thumbnail, label and caption
+        in the text
+
+        <div class="row fig" id="">
+            <a name=""></a>
+            <div class="col-md-4 col-sm-4">
+                <a href="2236-8906-hoehnea-49-e1112020-gf1.jpg" data-toggle="modal" data-target="#ModalFig">
+                    <div class="thumbImg">
+                        <img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
+            <div class="col-md-8 col-sm-8">
+                <strong>Figura 1.</strong>
+                <br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+            </div>
+        </div>
+        """
+        div_row_fig = self.html.find(
+            '//div[@class="row fig"]'
+        )
+        self.assertEqual("", div_row_fig.get("id"))
+        div_row_fig_divs = div_row_fig.xpath("div")
+
+        div_modal_fig_0_a = div_row_fig_divs[0].find("a")
+
+        # div_row_fig_divs[0] has link to image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig_0_a.get("href")
+        )
+        # div_row_fig_divs[0] has `@data-target` = #ModalFig
+        self.assertEqual(
+            "#ModalFig",
+            div_modal_fig_0_a.get("data-target")
+        )
+
+        # div_row_fig_divs[0] must have div[@class='thumbImg'] to display image
+        # as thumbnail
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig_0_a.find("div[@class='thumbImg']/img").get("src")
+        )
+
+        # div_modal_fig[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_fig_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Figura 1", texts)
+        self.assertIn(
+            "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
+
+    def test_fig_in_pannel_content(self):
+        """
+        Test de modal em tabs
+
+        <div class="tab-content">
+            <div role="tabpanel" class="tab-pane active" id="figures">
+
+        <div class="row fig">
+            <div class="col-md-4">
+                <a data-toggle="modal" data-target="#ModalFig">
+                    <div class="thumbImg">
+                        <img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        Thumbnail
+                        <div class="zoom">
+                            <span class="sci-ico-zoom"></span>
+                        </div>
+                    </div>
+                </a>
+            </div>
+            <div class="col-md-8">
+                <strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+        </div>
+        </div>
+        """
+        div_tab_panel = self.html.find(
+            './/div[@class="tab-content"]'
+        )
+        div_tab_panel = div_tab_panel.find(
+            './/div[@class="tab-pane active"]'
+        )
+        self.assertEqual("figures", div_tab_panel.get("id"))
+
+        div_row_fig = div_tab_panel.find(
+            './/div[@class="row fig"]'
+        )
+        div_row_fig_divs = div_row_fig.xpath("./div")
+
+        div_row_fig_div_0_a = div_row_fig_divs[0].find("a")
+
+        # div_row_fig_divs[0] has link to image path
+        self.assertEqual(
+            "modal",
+            div_row_fig_div_0_a.get("data-toggle")
+        )
+        # div_row_fig_divs[0] has `@data-target` = #ModalFig
+        self.assertEqual(
+            "#ModalFig",
+            div_row_fig_div_0_a.get("data-target")
+        )
+
+        # div_row_fig_divs[0] must have div[@class='thumbImg'] to display image
+        # as thumbnail
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_row_fig_div_0_a.find("div[@class='thumbImg']/img").get("src")
+        )
+
+        # div_modal_fig[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_fig_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Figura 1", texts)
+        self.assertIn(
+            "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
+

From 869b9cf9212021a0383e0e1707748f3fe9e016bf Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Fri, 25 Feb 2022 20:14:41 -0300
Subject: [PATCH 14/17] Inclui testes pra `fig[@id]`

---
 tests/test_htmlgenerator.py | 206 ++++++++++++++++++++++++++++++++++++
 1 file changed, 206 insertions(+)

diff --git a/tests/test_htmlgenerator.py b/tests/test_htmlgenerator.py
index 02bf73cf8..da21362f1 100644
--- a/tests/test_htmlgenerator.py
+++ b/tests/test_htmlgenerator.py
@@ -1598,3 +1598,209 @@ def test_fig_in_pannel_content(self):
         self.assertIn(
             "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
 
+
+class HTMLGeneratorFigWithIdTests(unittest.TestCase):
+
+    def setUp(self):
+        sample = u"""<article
+                      xmlns:mml="http://www.w3.org/1998/Math/MathML"
+                      xmlns:xlink="http://www.w3.org/1999/xlink"
+                      xml:lang="pt">
+                      <body>
+        <fig id="f1">
+            <label>Figura 1.</label>
+            <caption>
+                <title>Correlação entre o teor de fenóis totais e CE50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+            </caption>
+            <graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf1.jpg"/>
+            <attrib><xref ref-type="fig" rid="f1">Figure 1</xref>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+        </fig>
+        </body></article>
+        """
+        et = get_xml_tree_from_string(sample)
+        self.html = domain.HTMLGenerator.parse(et, valid_only=False).generate('pt')
+        # print(etree.tostring(self.html))
+
+    def test_fig_modal(self):
+        """
+        Test de modal
+        <div class="modal fade ModalFigs" id="ModalFigf1" tabindex="-1" role="dialog" aria-hidden="true">
+            <div class="modal-dialog modal-lg">
+            <div class="modal-content">
+                <div class="modal-header">
+                    <button type="button" class="close" data-dismiss="modal">
+                    <span aria-hidden="true">×</span><span class="sr-only">Close</span></button>
+                    <a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <span class="sci-ico-newWindow"></span>
+                    </a>
+                    <h4 class="modal-title">
+                        <span class="sci-ico-fileFigure"></span>Figura 1.   Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+                    </h4>
+                </div>
+                <div class="modal-body">
+                    <a href="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                    </a>
+                    <small>
+                        <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1">
+                            <span class="sci-ico-fileFigure"></span>Figure 1</a>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+                </div>
+            </div>
+            </div>
+        </div>
+        """
+        # div[@id='ModalFig'] (sem id)
+        div_modal_fig = self.html.find('.//div[@id="ModalFigf1"]')
+
+        # class="modal-header" has href with figure path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-header']/a").get("href")
+        )
+
+        # class="modal-title" has label and caption content
+        text = etree.tostring(
+            div_modal_fig.find('.//h4[@class="modal-title"]'),
+            encoding="utf-8"
+        ).decode("utf-8")
+
+        self.assertIn("Figura 1", text)
+        self.assertIn("Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", text)
+
+        # class="modal-body" has link to image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-body']/a").get("href")
+        )
+
+        # class="modal-body" has src with image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig.find(".//div[@class='modal-body']/a/img").get("src")
+        )
+
+        # class="modal-body" has `attrib` text presented inner `<small/>`
+        small = div_modal_fig.find(".//div[@class='modal-body']/small")
+        self.assertIn(
+            "Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.",
+            etree.tostring(small, encoding="utf-8").decode("utf-8")
+        )
+
+    def test_fig_in_text__thumbnail_and_label(self):
+        """
+        Test the html expected to display thumbnail, label and caption
+        in the text
+
+        <div class="row fig" id="">
+            <a name=""></a>
+            <div class="col-md-4 col-sm-4">
+                <a href="2236-8906-hoehnea-49-e1112020-gf1.jpg" data-toggle="modal" data-target="#ModalFig">
+                    <div class="thumbImg">
+                        <img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
+            <div class="col-md-8 col-sm-8">
+                <strong>Figura 1.</strong>
+                <br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+            </div>
+        </div>
+        """
+        div_row_fig = self.html.find(
+            '//div[@class="row fig"]'
+        )
+        self.assertEqual("f1", div_row_fig.get("id"))
+        div_row_fig_divs = div_row_fig.xpath("div")
+
+        div_modal_fig_0_a = div_row_fig_divs[0].find("a")
+
+        # div_row_fig_divs[0] has link to image path
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig_0_a.get("href")
+        )
+        # div_row_fig_divs[0] has `@data-target` = #ModalFig
+        self.assertEqual(
+            "#ModalFigf1",
+            div_modal_fig_0_a.get("data-target")
+        )
+
+        # div_row_fig_divs[0] must have div[@class='thumbImg'] to display image
+        # as thumbnail
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_modal_fig_0_a.find("div[@class='thumbImg']/img").get("src")
+        )
+
+        # div_modal_fig[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_fig_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Figura 1", texts)
+        self.assertIn(
+            "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
+
+    def test_fig_in_pannel_content(self):
+        """
+        Test de modal em tabs
+
+        <div class="tab-content">
+            <div role="tabpanel" class="tab-pane active" id="figures">
+
+        <div class="row fig">
+            <div class="col-md-4">
+                <a data-toggle="modal" data-target="#ModalFig">
+                    <div class="thumbImg">
+                        <img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        Thumbnail
+                        <div class="zoom">
+                            <span class="sci-ico-zoom"></span>
+                        </div>
+                    </div>
+                </a>
+            </div>
+            <div class="col-md-8">
+                <strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+        </div>
+        </div>
+        """
+        div_tab_panel = self.html.find(
+            './/div[@class="tab-content"]'
+        )
+        div_tab_panel = div_tab_panel.find(
+            './/div[@class="tab-pane active"]'
+        )
+        self.assertEqual("figures", div_tab_panel.get("id"))
+
+        div_row_fig = div_tab_panel.find(
+            './/div[@class="row fig"]'
+        )
+        div_row_fig_divs = div_row_fig.xpath("./div")
+
+        div_row_fig_div_0_a = div_row_fig_divs[0].find("a")
+
+        # div_row_fig_divs[0] has link to image path
+        self.assertEqual(
+            "modal",
+            div_row_fig_div_0_a.get("data-toggle")
+        )
+        # div_row_fig_divs[0] has `@data-target` = #ModalFig
+        self.assertEqual(
+            "#ModalFigf1",
+            div_row_fig_div_0_a.get("data-target")
+        )
+
+        # div_row_fig_divs[0] must have div[@class='thumbImg'] to display image
+        # as thumbnail
+        self.assertEqual(
+            "2236-8906-hoehnea-49-e1112020-gf1.jpg",
+            div_row_fig_div_0_a.find("div[@class='thumbImg']/img").get("src")
+        )
+
+        # div_modal_fig[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_fig_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Figura 1", texts)
+        self.assertIn(
+            "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
+

From 44c6a1f883ab0faeba4aaea6c89914ab13dae6cd Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Fri, 25 Feb 2022 21:12:02 -0300
Subject: [PATCH 15/17] Cria testes para `table-wrap[@id]`

---
 tests/test_htmlgenerator.py | 241 ++++++++++++++++++++++++++++++++++++
 1 file changed, 241 insertions(+)

diff --git a/tests/test_htmlgenerator.py b/tests/test_htmlgenerator.py
index da21362f1..5534a890b 100644
--- a/tests/test_htmlgenerator.py
+++ b/tests/test_htmlgenerator.py
@@ -1804,3 +1804,244 @@ def test_fig_in_pannel_content(self):
         self.assertIn(
             "Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.", texts)
 
+
+class HTMLGeneratorTableWrapWithIdTests(unittest.TestCase):
+
+    def setUp(self):
+        sample = u"""<article
+                      xmlns:mml="http://www.w3.org/1998/Math/MathML"
+                      xmlns:xlink="http://www.w3.org/1999/xlink"
+                      xml:lang="pt">
+                      <body>
+        <table-wrap id="t1">
+            <label>Tabela 1.</label>
+            <caption>
+                <title>Identificação das espécies de <italic>Senna</italic> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</title>
+            </caption>
+            <table>
+                <colgroup>
+                    <col/>
+                    <col/>
+                    <col/>
+                    <col/>
+                </colgroup>
+                <thead>
+                    <tr>
+                        <th align="left">Espécies</th>
+                        <th align="left">Nome popular</th>
+                        <th align="center">Local de coleta</th>
+                        <th align="center">No. HUVA</th>
+                    </tr>
+                </thead>
+                <tbody>
+                    <tr>
+                        <td align="left"><italic>S. alata</italic> (L.) Roxb.</td>
+                        <td align="left">fedegoso-gigante</td>
+                        <td align="center">Sobral</td>
+                        <td align="center">21547</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. obtusifolia</italic> (L.) H.S.Irwin &amp; Barneby</td>
+                        <td align="left">fedegoso-brando</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21775</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. occidentalis</italic> (L.) Link</td>
+                        <td align="left">café-negro</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21774</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. siamea</italic> (Lam.) H.S.Irwin &amp; Barneby<sup>*</sup></td>
+                        <td align="left">cássia-de-sião</td>
+                        <td align="center">Sobral</td>
+                        <td align="center">21578</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. trachypus</italic> (Benth.) H.S.Irwin &amp; Barneby<sup>**</sup></td>
+                        <td align="left">pau-de-besouro</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21776</td>
+                    </tr>
+                </tbody>
+            </table>
+            <table-wrap-foot>
+                <fn id="TFN1">
+                    <p><xref ref-type="table" rid="t1">Table 1</xref>Identification of <italic>Senna Senna</italic> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</p>
+                </fn>
+            </table-wrap-foot>
+        </table-wrap>
+
+        </body></article>
+        """
+        et = get_xml_tree_from_string(sample)
+        self.html = domain.HTMLGenerator.parse(et, valid_only=False).generate('pt')
+        # print(etree.tostring(self.html))
+
+    def test_table_wrap_modal(self):
+        """
+        Test de modal
+
+        <div class="modal fade ModalTables" id="ModalTablet1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+        <div class="modal-header">
+        <button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+        <span class="sci-ico-fileTable"></span><strong>Tabela 1.</strong>    Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
+        </h4>
+        </div>
+        <div class="modal-body"><div class="table table-hover"><table>
+        <colgroup>
+        <col>
+        <col>
+        <col>
+        <col>
+        </colgroup>
+        <thead><tr>
+        <th align="left">Espécies</th>
+        <th align="left">Nome popular</th>
+        <th align="center">Local de coleta</th>
+        <th align="center">No. HUVA</th>
+        </tr></thead>
+        <tbody>
+        <tr>
+        <td align="left">
+        <i>S. alata</i> (L.) Roxb.</td>
+        <td align="left">fedegoso-gigante</td>
+        <td align="center">Sobral</td>
+        <td align="center">21547</td>
+        </tr>
+        </tbody>
+        </table></div></div>
+        <div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+        <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>Table 1</a>Identification of <i>Senna Senna</i> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</div></li></ul></div></div>
+        </div></div></div>
+        """
+        # div[@id='ModalFig'] (sem id)
+        div_modal = self.html.find('.//div[@id="ModalTablet1"]')
+
+        # class="modal-title" has label and caption content
+        text = etree.tostring(
+            div_modal.find('.//h4[@class="modal-title"]'),
+            encoding="utf-8"
+        ).decode("utf-8")
+
+        self.assertIn("Tabela 1", text)
+        self.assertIn("Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).", text)
+
+        # class="modal-body" has link to image path
+        self.assertIsNotNone(
+            div_modal.find(".//div[@class='modal-body']//table")
+        )
+
+        # class="modal-body" has `attrib` text presented inner `<small/>`
+        footer = div_modal.find(".//div[@class='modal-footer']")
+        self.assertIn(
+            "Identification of <i>Senna Senna</i> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).",
+            etree.tostring(footer, encoding="utf-8").decode("utf-8")
+        )
+
+    def test_table_wrap_in_text__thumbnail_and_label(self):
+        """
+        Test the html expected to display thumbnail, label and caption
+        in the text
+
+        <div class="row table" id="t1">
+            <a name="t1"></a>
+            <div class="col-md-4 col-sm-4">
+                <a data-toggle="modal" data-target="#ModalTablet1">
+                    <div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                    </div>
+                </a>
+            </div>
+            <div class="col-md-8 col-sm-8">
+            <strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
+            </div>
+        </div>
+        """
+        div_row_table = self.html.find(
+            '//div[@class="row table"]'
+        )
+        self.assertEqual("t1", div_row_table.get("id"))
+        div_row_table_divs = div_row_table.xpath("div")
+
+        div_modal_table_0_a = div_row_table_divs[0].find("a")
+
+        # div_row_table_divs[0] has `@data-target` = #ModalTablet1
+        self.assertEqual(
+            "#ModalTablet1",
+            div_modal_table_0_a.get("data-target")
+        )
+
+        # div_row_table_divs[0] must have div[@class='thumbImg'] to display image
+        # as thumbnail
+        self.assertIsNotNone(
+            div_modal_table_0_a.find("div[@class='thumbOff']")
+        )
+
+        # div_modal_table[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_table_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Tabela 1.", texts)
+        self.assertIn(
+            "Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).", texts)
+
+    def test_table_wrap_in_pannel_content(self):
+        """
+        Test de modal em tabs
+
+        <div role="tabpanel" class="tab-pane " id="tables">
+            <div class="row table">
+                <div class="col-md-4">
+                    <a data-toggle="modal" data-target="#ModalTablet1">
+                        <div class="thumbOff">
+                            Thumbnail
+                            <div class="zoom"><span class="sci-ico-zoom"></span></div>
+                        </div>
+                    </a>
+                </div>
+                <div class="col-md-8">
+                    <strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</div>
+            </div>
+        </div>
+        """
+        div_tab_panel = self.html.find(
+            './/div[@class="tab-content"]'
+        )
+        div_tab_panel = div_tab_panel.find(
+            './/div[@class="tab-pane active"]'
+        )
+        self.assertEqual("tables", div_tab_panel.get("id"))
+
+        div_row_table = div_tab_panel.find(
+            './/div[@class="row table"]'
+        )
+        div_row_table_divs = div_row_table.xpath("./div")
+
+        div_row_table_div_0_a = div_row_table_divs[0].find("a")
+
+        # div_row_table_divs[0] has link to image path
+        self.assertEqual(
+            "modal",
+            div_row_table_div_0_a.get("data-toggle")
+        )
+        # div_row_table_divs[0] has `@data-target` = #ModalFig
+        self.assertEqual(
+            "#ModalTablet1",
+            div_row_table_div_0_a.get("data-target")
+        )
+
+        # div_row_table_divs[0] must have div[@class='thumbOff'] to display image
+        # as thumbnail
+        self.assertIsNotNone(
+            div_row_table_div_0_a.find("div[@class='thumbOff']")
+        )
+
+        # div_modal_table[1] has label and caption texts
+        texts = etree.tostring(
+            div_row_table_divs[1], encoding="utf-8").decode("utf-8")
+        self.assertIn("Tabela 1.", texts)
+        self.assertIn(
+            "Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).", texts)
+

From 52c8c48180f9fa1a8e5b056c17d653a2e782a9f2 Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Fri, 25 Feb 2022 21:31:03 -0300
Subject: [PATCH 16/17] =?UTF-8?q?Cria=20teste=20para=20o=20modal=20que=20c?=
 =?UTF-8?q?ont=C3=A9m=20as=20abas=20para=20figuras=20e=20tabelas?=
MIME-Version: 1.0
Content-Type: text/plain; charset=UTF-8
Content-Transfer-Encoding: 8bit

---
 tests/test_htmlgenerator.py | 145 ++++++++++++++++++++++++++++++++++++
 1 file changed, 145 insertions(+)

diff --git a/tests/test_htmlgenerator.py b/tests/test_htmlgenerator.py
index 5534a890b..b6d50a5cd 100644
--- a/tests/test_htmlgenerator.py
+++ b/tests/test_htmlgenerator.py
@@ -2045,3 +2045,148 @@ def test_table_wrap_in_pannel_content(self):
         self.assertIn(
             "Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).", texts)
 
+
+
+class HTMLGeneratorModalWithFiguresAndTablesTests(unittest.TestCase):
+
+    def setUp(self):
+        sample = u"""<article
+                      xmlns:mml="http://www.w3.org/1998/Math/MathML"
+                      xmlns:xlink="http://www.w3.org/1999/xlink"
+                      xml:lang="pt">
+                      <body>
+        <fig id="f1">
+            <label>Figura 1.</label>
+            <caption>
+                <title>Correlação entre o teor de fenóis totais e CE50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+            </caption>
+            <graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf1.jpg"/>
+            <attrib><xref ref-type="fig" rid="f1">Figure 1</xref>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+        </fig>
+        <table-wrap id="t1">
+            <label>Tabela 1.</label>
+            <caption>
+                <title>Identificação das espécies de <italic>Senna</italic> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</title>
+            </caption>
+            <table>
+                <colgroup>
+                    <col/>
+                    <col/>
+                    <col/>
+                    <col/>
+                </colgroup>
+                <thead>
+                    <tr>
+                        <th align="left">Espécies</th>
+                        <th align="left">Nome popular</th>
+                        <th align="center">Local de coleta</th>
+                        <th align="center">No. HUVA</th>
+                    </tr>
+                </thead>
+                <tbody>
+                    <tr>
+                        <td align="left"><italic>S. alata</italic> (L.) Roxb.</td>
+                        <td align="left">fedegoso-gigante</td>
+                        <td align="center">Sobral</td>
+                        <td align="center">21547</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. obtusifolia</italic> (L.) H.S.Irwin &amp; Barneby</td>
+                        <td align="left">fedegoso-brando</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21775</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. occidentalis</italic> (L.) Link</td>
+                        <td align="left">café-negro</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21774</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. siamea</italic> (Lam.) H.S.Irwin &amp; Barneby<sup>*</sup></td>
+                        <td align="left">cássia-de-sião</td>
+                        <td align="center">Sobral</td>
+                        <td align="center">21578</td>
+                    </tr>
+                    <tr>
+                        <td align="left"><italic>S. trachypus</italic> (Benth.) H.S.Irwin &amp; Barneby<sup>**</sup></td>
+                        <td align="left">pau-de-besouro</td>
+                        <td align="center">Graça</td>
+                        <td align="center">21776</td>
+                    </tr>
+                </tbody>
+            </table>
+            <table-wrap-foot>
+                <fn id="TFN1">
+                    <p><xref ref-type="table" rid="t1">Table 1</xref>Identification of <italic>Senna Senna</italic> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</p>
+                </fn>
+            </table-wrap-foot>
+        </table-wrap>
+        </body></article>
+        """
+        et = get_xml_tree_from_string(sample)
+        self.html = domain.HTMLGenerator.parse(et, valid_only=False).generate('pt')
+        # print(etree.tostring(self.html))
+
+    def test_tabs_modal(self):
+        """
+        Test de modal
+        
+        <div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true">
+            <div class="modal-dialog">
+                <div class="modal-content">
+                    <div class="modal-header">
+                        <button type="button" class="close" data-dismiss="modal">
+                            <span aria-hidden="true">×</span>
+                            <span class="sr-only">Close</span>
+                        </button>
+                        <h4 class="modal-title">Figuras | Tabelas</h4>
+                    </div>
+                    <div class="modal-body">
+                        <ul class="nav nav-tabs md-tabs" role="tablist">
+                            <li role="presentation" class="col-md-4 col-sm-4 active">
+                                <a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">Figuras (1)</a>
+                            </li>
+                            <li role="presentation" class="col-md-4 col-sm-4 ">
+                                <a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">Tabelas (1)</a></li>
+                        </ul>
+                    </div>
+                </div>
+            </div>
+        </div>
+        """
+        # div[@id='ModalFig'] (sem id)
+        div_modal = self.html.find('.//div[@id="ModalTablesFigures"]')
+
+        h4 = div_modal.find(".//div[@class='modal-header']/h4")
+        text = etree.tostring(h4, encoding="utf-8").decode("utf-8")
+        self.assertIn("Figuras | Tabelas", text)
+
+        # class="modal-title" has label and caption content
+        text = etree.tostring(
+            div_modal.find('.//h4[@class="modal-title"]'),
+            encoding="utf-8"
+        ).decode("utf-8")
+
+        # modal-body
+        modal_body = div_modal.find('.//div[@class="modal-body"]')
+        li = modal_body.findall(".//li")
+        self.assertEqual(len(li), 2)
+
+        fig_text = etree.tostring(li[0], encoding="utf-8").decode("utf-8")
+        fig_text = " ".join([w for w in fig_text.split()])
+        self.assertIn("Figuras (1)", fig_text)
+
+        a = li[0].find("a")
+        self.assertEqual(a.get("href"), "#figures")
+        self.assertEqual(a.get("aria-controls"), "figures")
+        self.assertEqual(a.get("data-toggle"), "tab")
+
+        table_text = etree.tostring(li[1], encoding="utf-8").decode("utf-8")
+        table_text = " ".join([w for w in table_text.split()])
+        self.assertIn("Tabelas (1)", table_text)
+
+        a = li[1].find("a")
+        self.assertEqual(a.get("href"), "#tables")
+        self.assertEqual(a.get("aria-controls"), "tables")
+        self.assertEqual(a.get("data-toggle"), "tab")

From 91f820abeae87fda298d69d49288e0f0e36ae78b Mon Sep 17 00:00:00 2001
From: Roberta Takenaka <roberta.takenaka@scielo.org>
Date: Wed, 2 Mar 2022 09:55:47 -0300
Subject: [PATCH 17/17] Inclui fixtures para as fig-group e table-wrap-group

---
 .../2236-8906-hoehnea-49-e1112020-gf1.jpg     |  Bin 0 -> 11375 bytes
 .../2236-8906-hoehnea-49-e1112020-gf2.jpg     |  Bin 0 -> 11057 bytes
 .../2236-8906-hoehnea-49-e1112020-gf3.jpg     |  Bin 0 -> 11319 bytes
 .../2236-8906-hoehnea-49-e1112020.pdf         |  Bin 0 -> 436834 bytes
 .../2236-8906-hoehnea-49-e1112020.pt.html     | 1019 ++++++
 .../2236-8906-hoehnea-49-e1112020.xml         | 2597 +++++++++++++++
 .../expected.html                             | 1019 ++++++
 .../2236-8906-hoehnea-49-e1082020.pt.html     | 2386 ++++++++++++++
 .../2236-8906-hoehnea-49-e1082020.xml         | 2890 +++++++++++++++++
 .../expected.html                             | 2386 ++++++++++++++
 10 files changed, 12297 insertions(+)
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020-gf1.jpg
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020-gf2.jpg
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020-gf3.jpg
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020.pdf
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020.pt.html
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020.xml
 create mode 100644 tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/expected.html
 create mode 100644 tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/2236-8906-hoehnea-49-e1082020.pt.html
 create mode 100644 tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/2236-8906-hoehnea-49-e1082020.xml
 create mode 100644 tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/expected.html

diff --git a/tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020-gf1.jpg b/tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020-gf1.jpg
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+<title></title>
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+<div class="articleBadge-editionMeta-doi-copyLink">
+<span class="_articleBadge">Artigo</span><span class="_separator"> • </span><span class="_editionMeta">Hoehnea 49 <span class="_separator"> • </span>2022</span><span class="_separator"> • </span><span class="group-doi"><a href="https://doi.org/10.1590/2236-8906-111/2020" class="_doi" target="_blank">https://doi.org/10.1590/2236-8906-111/2020</a>
+         
+        <a class="copyLink" data-clipboard-text="https://doi.org/10.1590/2236-8906-111/2020"><span class="sci-ico-link"></span>copiar</a></span>
+</div>
+<h1 class="article-title">
+<span class="sci-ico-openAccess showTooltip" data-toggle="tooltip" data-original-title="by 4.0 "></span>Prospecção química, atividade antioxidante, anticolinesterásica e antifúngica de extratos etanólicos de espécies de <i>Senna</i> Mill. (Fabaceae)<a id="shorten" href="#" class="short-link"><span class="sci-ico-link"></span></a>
+</h1>
+<h2 class="article-title">Chemical prospecting and antioxidant, anticholinesterase and antifungal activity of ethanol extracts from <i>Senna</i> Mill. species. (Fabaceae)</h2>
+<div class="articleMeta"></div>
+<div class="contribGroup">
+<span class="dropdown"><a id="contribGroupTutor1" class="dropdown-toggle" data-toggle="dropdown"><span> Andréa Maria Neves </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor1">
+<strong></strong> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil<div class="corresp">
+					<h3><sup>4</sup></h3> Autor para correspondência: <a href="mailto:andreamarianeves@gmail.com">andreamarianeves@gmail.com</a>
+				</div>
+<a href="http://orcid.org/0000-0002-7388-1844" class="btnContribLinks orcid">http://orcid.org/0000-0002-7388-1844</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor2" class="dropdown-toggle" data-toggle="dropdown"><span> Selene Maia de Morais </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor2">
+<strong></strong> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil<a href="http://orcid.org/0000-0002-2766-3790" class="btnContribLinks orcid">http://orcid.org/0000-0002-2766-3790</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor3" class="dropdown-toggle" data-toggle="dropdown"><span> Hélcio Silva dos Santos </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor3">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Exatas e Tecnologia, Curso de Química, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0001-5527-164X" class="btnContribLinks orcid">http://orcid.org/0000-0001-5527-164X</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor4" class="dropdown-toggle" data-toggle="dropdown"><span> Marcílio Matos Ferreira </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor4">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0003-2503-9772" class="btnContribLinks orcid">http://orcid.org/0000-0003-2503-9772</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor5" class="dropdown-toggle" data-toggle="dropdown"><span> Ricardo Carneiro Vera Cruz </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor5">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-2035-0425" class="btnContribLinks orcid">http://orcid.org/0000-0002-2035-0425</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor6" class="dropdown-toggle" data-toggle="dropdown"><span> Elnatan Bezerra de Souza </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor6">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-5222-4378" class="btnContribLinks orcid">http://orcid.org/0000-0002-5222-4378</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor7" class="dropdown-toggle" data-toggle="dropdown"><span> Lúcia Betânia da Silva Andrade </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor7">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-4384-5738" class="btnContribLinks orcid">http://orcid.org/0000-0002-4384-5738</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor8" class="dropdown-toggle" data-toggle="dropdown"><span> Raquel Oliveira dos Santos Fontenelle </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor8">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-8865-5954" class="btnContribLinks orcid">http://orcid.org/0000-0002-8865-5954</a>
+</ul></span><a href="" class="outlineFadeLink" data-toggle="modal" data-target="#ModalTutors">Sobre os autores</a>
+</div>
+<div class="row">
+<ul class="col-md-2 hidden-sm articleMenu"></ul>
+<article id="articleText" class="col-md-10 col-md-offset-2 col-sm-12 col-sm-offset-0"><div class="articleSection" data-anchor="RESUMO">
+<h1 class="articleSectionTitle">RESUMO</h1>
+<p>O objetivo deste trabalho foi avaliar o perfil químico, teor de fenóis totais e as atividades antioxidante, antiacetilcolinesterásica e antifúngica dos extratos etanólicos das folhas (EEF) e do caule (EEC) de cinco espécies de <i>Senna</i>, bem como avaliar a correlação entre o conteúdo de fenóis totais com a atividade sequestradora do radical livre DPPH e com a inibição da enzima acetilcolinesterase AChEI. No teste fitoquímico, evidenciou-se a presença de metabólitos secundários em todos os extratos. Os EEF e EEC de <i>Senna trachypus</i>, destacaram-se por apresentar os maiores valores de fenóis totais. Os EEF e EEC de <i>S. trachypus</i> mostraram a melhor ação sobre a enzima acetilcolinesterase. Todas as espécies apresentaram atividade antioxidante, em especial o EEF de <i>S. trachypus</i>. Foi observado correlação forte para as variáveis fenóis totais e atividade antioxidante (r = -0,71), muito forte para fenóis totais e antiacetilcolinesterase (r = -0,84) e atividade moderada para atividade antioxidante e antiacetilcolinesterase (0,43). Apenas os extratos de <i>S. trachypus</i> apresentaram atividade contra todos os dermatófitos, quando comparado às demais espécies. A espécie <i>S. trachypus</i> foi considerada a planta mais promissora para estudos subsequentes, a fim de encontrar compostos com ações farmacológicas. </p>
+<p><strong>Palavras-chave:</strong><br>acetilcolinesterase; dermatófitos; fitoquímica; produtos naturais; radicais livres</p>
+</div>
+<div class="articleSection" data-anchor="ABSTRACT">
+<h1 class="articleSectionTitle">ABSTRACT</h1>
+<p>The objective of this work was to evaluate the chemical profile, total phenol content and the antioxidant, antiacetylcholinesterase and antifungal activities of ethanol extracts from leaves (EEF) and stem (EEC) of five species of <i>Senna</i>, as well as to evaluate the correlation between the content of total phenols with the DPPH free radical scavenging activity and with the inhibition of the acetylcholinesterase AChEI enzyme. The phytochemical test showed the presence of secondary metabolites in all extracts. The EEF and EEC of <i>Senna trachypus</i>, stood out for presenting the highest values of total phenols. <i>S. trachypus</i> EEF and EEC showed the best action on the acetylcholinesterase enzyme. All species showed antioxidant activity, especially the EEF from <i>S. trachypus</i>. A strong correlation was observed for the variables total phenols and antioxidant activity (r = -0.71), very strong for total phenols and anti-acetylcholinesterase (r = -0.84) and moderate activity for antioxidant and anti-acetylcholinesterase activity (r = 0.43). Only <i>S. trachypus</i> extracts showed activity against all dermatophytes, when compared to the other species. The species <i>S. trachypus</i> was considered the most promising plant for further studies, in order to find compounds with pharmacological actions.</p>
+<p><strong>Keywords:</strong><br>acetylcholinesterase; dermatophytes; phytochemistry; natural products; free radicals</p>
+</div>
+<div class="articleSection" data-anchor="Text">
+<h1 class="articleSectionTitle">Introdução</h1>
+<p><i>Senna</i> Mill. é um gênero monofilético com distribuição pantropical e ampla variedade morfológica (<span class="ref"><strong class="xref xrefblue">Pellerin <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Pellerin, R.J., Waminal, N.E. &amp; Kim, H.H. 2019. FISH mapping of rDNA and telomeric repeats in 10 Senna species. Horticulture, Environment, and Biotechnology 60: 253-260.</span></span></span>). Possuindo aproximadamente 300 espécies, das quais 200 nas Américas, este gênero é o segundo maior da família Fabaceae (<span class="ref"><strong class="xref xrefblue">Queiroz 2009</strong><span class="refCtt closed"><span>Queiroz, L.P. 2009. Leguminosas da Caatinga. Universidade Estadual de Feira de Santana, Feira de Santana, 467 p.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kim <i>et al</i>. 2018</strong><span class="refCtt closed"><span>Kim, M.S., Lee, D.Y., Sung, S.H. &amp; Jeon, W.K. 2018. Anti-cholinesterase activities of hydrolysable tannins and polyhydroxytriterpenoid derivatives from Terminalia chebula Retz. fruit. Fruit Rec Nat Prod 12: 284-289.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Souza &amp; Silva 2016</strong><span class="refCtt closed"><span>Souza, A.O. &amp; Silva, M.J. 2016. Senna (Leguminosae, Caesalpinioideae) na Floresta Nacional de Silvânia, Goiás, Brasil. Rodriguésia 67: 773-784. </span></span></span>). O gênero é representado no Brasil por 79 espécies, onde 29 são endêmicas, sendo a região Nordeste a que apresenta a maior riqueza de espécies com 53 registros (<span class="ref"><strong class="xref xrefblue">BFG 2018</strong><span class="refCtt closed"><span>BFG. 2018. Brazilian Flora 2020: Innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 1513-1527. </span></span></span>). </p>
+<p>Trata-se de um gênero muito expressivo na flora do semiárido, alcançando destaque no Domínio Fitogeográfico da Caatinga, onde são catalogadas 42 espécies (<span class="ref"><strong class="xref xrefblue">Souza &amp; Bortoluzzi 2015</strong><span class="refCtt closed"><span>Souza, V.C.; Bortoluzzi, R.L.C. 2015. Senna in Lista de Espécies da Flora do Brasil. Jardim Botânico do Rio de Janeiro. </span></span></span>). As espécies de <i>Senna</i> são geralmente arbustos ou arvoretas, raramente ervas ou subarbustos anuais. Entre as suas características diagnósticas estão os nectários extraflorais convexos, interfoliolares, flores vistosas, com pétalas amarelo-brilhantes, anteras amarelas, rígidas, com deiscência abrindo por poros ou fendas, ausência de bractéolas no pedicelo, frutos deiscentes plano-compressos ou indeiscentes e cilíndricos (<span class="ref"><strong class="xref xrefblue">Queiroz 2009</strong><span class="refCtt closed"><span>Queiroz, L.P. 2009. Leguminosas da Caatinga. Universidade Estadual de Feira de Santana, Feira de Santana, 467 p.</span></span></span>).</p>
+<p>As espécies de <i>Senna</i> têm diversas aplicações medicinais e são eficazes no tratamento para uma série de doenças, como malária, micose, dengue, eczema, hepatite e dermatite, sendo também indicadas como anti-hipertensivo, vermífugo, laxante, abortivo e antitussígeno (<span class="ref"><strong class="xref xrefblue">Macedo <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Macedo, E.M., Alan, J.G., &amp; Silva, M.G.V. 2016. Quimiodiversidade e propriedades biofarmacológicas de espécies de Senna nativas do Nordeste do Brasil. Revista Virtual de Química 8: 169-195.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bieski <i>et al</i>. 2015</strong><span class="refCtt closed"><span>Bieski, I.G.C., Leonti, M., Arnason, J.T., Ferrier, J., Rapinski, M., Violante, I.M.P., Balogun,S.O., Pereira, J.F.C.A., Figueiredo, R.D.C.F., Lopes, C.R.A.S., Silva, D.R.D., Pacini, A., Albuquerque, U.P. &amp; Martins, D.T.D.O. 2015. Ethnobotanical study of medicinal plants by population of valley of Juruena region, legal amazon, Mato Grosso, Brazil. Journal of Ethnopharmacology 173: 383-423.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kabir <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Kabir, M.H., Hasan, N., Rahman, M.M., Rahman, M.A., Khan, J.A., Hoque, N.T., Bhuiyan, M.R.Q., Mou, S.M.; Jahan, R. &amp; Rahmatullah, M. 2014. A survey of medicinal plants used by the Deb barma clan of the Tripura tribe of Moulvibazar district, Bangladesh. Journal of Ethnobiology and Ethnomedicine 10: 1-19.</span></span></span>). Além de suas aplicações farmacológicas, estudos têm revelado que espécies pertencentes a este gênero possuem, em sua composição, uma vasta diversidade de princípios bioativos que estão associadas a diferentes atividades biológicas. Neste sentido, podemos citar como exemplo as atividades antioxidantes, antitumoral, antibacterianas, antifúngicas e anti-inflamatórias (<span class="ref"><strong class="xref xrefblue">Neves <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Neves, A.M., Costa, O.S., Coutinho, M.G.S., Souza, E.B., Santos, H.S., Silva, M.G.V. &amp; Fontenelle, R.O.S. 2017. Caracterização química e o potencial antimicrobiano de espécies do gênero Senna Mill (Fabaceae). Rev. Virtual Quim 9: 2506-2538.</span></span></span>).</p>
+<p>As plantas são fontes alternativas promissoras de substâncias de interesse biológico e farmacológico, já que podem produzir, a partir de seu metabolismo secundário, uma enorme diversidade de substâncias, dentre estas, os compostos fenólicos. Alguns estudos têm revelado que os compostos fenólicos são responsáveis por várias atividades biológicas, incluindo atividade antifúngica. Esta atividade pode ser direta nos micro-organismos, ou sobre outros fatores necessários para a expressão da virulência ou patogenicidade (<span class="ref"><strong class="xref xrefblue">Rodrigues <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Rodrigues, F.C., Dos Santos, A.T.L., Machado, A.J.T., Bezerra, C.F., de Freitas, T.S., Coutinho, H.D.M., Morais-Braga, M.F.B., Bezerra, J.W.A., Duarte, A.E., Kamdem, J.P., Boligon, A.A., Campos, M.M.A., Barros, L.M. 2019. Chemical composition and anti-Candida potencial of the extracts of Tarenaya spinosa (Jacq.) Raf.(Cleomaceae). Comparative immunology, microbiology and infectious diseases 64: 14-19.</span></span></span>).</p>
+<p>Os compostos fenólicos estão entre os metabólitos secundários mais estudados, notadamente por possuírem grande potencial para atividades antioxidantes, atuando na redução do risco de algumas doenças agudas e crônicas relacionadas ao estado redox do corpo humano, ocasionadas pelos radicais livres. Estas moléculas apresentam uma alta capacidade reativa, sendo consideradas perigosas para os organismos vivos, causando doenças prejudiciais, incluindo doenças neurodegenerativas, como o mal de Alzheimer (DA). Atualmente, uma das teorias mais aceitas na abordagem padrão no tratamento sintomático dessa demência é a “hipótese colinérgica”. Portanto, os inibidores da enzima acetilcolinesterase (AChEI) preservam os níveis de acetilcolina, melhorando a eficiência da transmissão colinérgica (<span class="ref"><strong class="xref xrefblue">Bardakci <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Bardakci, H., CeleP, E., Gözet, T., Kan, Y. &amp; Kirmizibekmez, H. 2019. Phytochemical characterization and antioxidant activities of the fruit extracts of several Crataegus taxa. South African Journal of Botany 124: 5-13. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Lim <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Lim, S., Choi, A.H., Kwon, M., Joung, E.J., Shin, T., Lee, S.G., Kim, NG. &amp; Kim, H. R. 2019. Evaluation of antioxidant activities of various solvent extract from Sargassum serratifolium and its major antioxidant components. Food Chemistry 278: 178-184.</span></span></span>; <span class="ref"><strong class="xref xrefblue">Neagu <i>et al</i>. 2016</strong><span class="refCtt closed"><span>Neagu, E., Radu, G.L., Albu, C., &amp; Paun, G. 2016. Antioxidant activity, acetylcholinesterase and tyrosinase inhibitory potential of Pulmonaria officinalis and Centarium umbellatum extracts. Saudi Journal of Biological Sciences, 3: 578-585.</span></span></span>).</p>
+<p>Por este motivo, a utilização de dietas ricas ou enriquecidas com antioxidantes podem prevenir, ou pelo menos amenizar, a deterioração orgânica por um excessivo estresse oxidativo. Além disso, o crescimento sobre a investigação científica envolvendo os efeitos antioxidantes de extratos brutos, frações purificadas, ou mesmo de compostos isolados, onde estão classificados os compostos fenólicos, são demonstrados em muitos estudos (<span class="ref"><strong class="xref xrefblue">Penido <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Penido, A.B., De Morais, S.M., Ribeiro, A.B., Alves, D.R., Rodrigues, A.L.M., dos Santos, L.H. &amp; de Menezes, J.E.S.A. 2017. Medicinal plants from northeastern Brazil against Alzheimer’s disease. Evidence-Based Complementary and Alternative Medicine 2017: 1-7. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Morais <i>et al.</i> 2013</strong><span class="refCtt closed"><span>Morais, S.M., Lima, K.S.B., Siqueira, S.M.C., Cavalcanti, E.S.B., Souza, M.S.T., Menezes, J.E.S.A., Trevisan, M.T.S. 2013. Correlação entre as atividades antiradical, antiacetilcolinesterase e teor de fenóis totais de extratos de plantas medicinais de farmácias vivas. Revista Brasileira de Plantas Medicinais 15: 575-582. </span></span></span>).</p>
+<p>Desta forma, investigar a atividade antifúngica e anticolinesterásica de extratos de espécies de <i>Senna</i>, analisando o seu potencial antioxidante, o seu teor de fenóis totais e o seu perfil fitoquímico, são maneiras de promover tanto o conhecimento acerca dessas espécies, como também potencializar o descobrimento de novos fitofármacos para o combate de inúmeras enfermidades. Assim, este trabalho avaliou o perfil fitoquímico, o teor de fenóis totais e as atividades antioxidante, anticolinesterásica e antifúngica dos extratos etanólicos de <i>S. alata</i> (L.) Roxb., <i>S. obtusifolia</i> (L.) H.S.Irwin &amp; Barneby, <i>S. occidentalis</i> (L.) Link, <i>S. siamea</i> (Lam.) H.S.Irwin &amp; Barneby e <i>S. trachypus</i> (Benth.) H.S.Irwin &amp; Barneby, e a correlação entre o teor de fenóis totais e as atividades antioxidante e anticolinesterásica. </p>
+<h1 class="articleSectionTitle">Materiais e métodos</h1>
+<p>Material vegetal e preparação dos extratos - Foram selecionadas para este estudo cinco espécies de <i>Senna</i>, sendo uma exótica naturalizada e quatro nativas, das quais uma é endêmica do Brasil, ocorrendo no Cerrado e na Caatinga (<span class="ref"><strong class="xref xrefblue">BFG 2018</strong><span class="refCtt closed"><span>BFG. 2018. Brazilian Flora 2020: Innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 1513-1527. </span></span></span>) (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>Tabela 1</a>). As folhas e caules de <i>Senna</i> spp. foram coletados em diferentes locais da região Noroeste do Ceará. A identificação botânica das espécies foi realizada no Herbário Francisco José de Abreu Matos da Universidade Estadual Vale do Acaraú (HUVA), pelo professor Dr. Elnatan Bezerra de Souza. Para o preparo dos extratos, 200g das folhas e caule secos de cada espécie de um mesmo indivíduo foram triturados e imersos durante 10 dias em 500 mL de etanol e, na sequência o extrato foi filtrado e concentrado em um evaporador rotativo a (60°C) durante 2 h. Após este processo, foi mantido em banho-maria (40°C) até a eliminação total do solvente, obtendo-se o extrato etanólico das folhas (EEF) e extrato etanólico do caule (EEC) (<span class="ref"><strong class="xref xrefblue">Matos 2009</strong><span class="refCtt closed"><span>Matos, F.J.A. 2009. Introdução à Fitoquímica Experimental. 3 ed. Fortaleza: UFC. 150p.</span></span></span>).</p>
+<div>
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+<strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
+</div>
+</div>
+			</div>
+<p>Triagem fitoquímica - Os extratos etanólicos foram submetidos a triagem fitoquímica, tomando como referência a metodologia descrita por <span class="ref"><strong class="xref xrefblue">Matos (2009</strong><span class="refCtt closed"><span>Matos, F.J.A. 2009. Introdução à Fitoquímica Experimental. 3 ed. Fortaleza: UFC. 150p.</span></span></span>). Através deste ensaio preliminar, foi possível verificar as principais classes de metabólitos secundários por meio de reações químicas que resultaram no aparecimento de coloração e/ou precipitado, característico para cada classe de substância. Os ensaios foram conduzidos para as seguintes classes de substâncias: fenóis, taninos, flavonoides, saponinas, esteroides, triterpenoides e alcaloides. Todos os testes foram realizados em triplicata procedimentais. </p>
+<p>Determinação do teor de fenóis totais - O teor de fenóis totais nos extratos etanólicos foi determinado pelo método espectrofotométrico de Folin-Ciocateau, utilizando ácido gálico como padrão de referência (<span class="ref"><strong class="xref xrefblue">Kim <i>et al.</i> 2006</strong><span class="refCtt closed"><span>Kim, K.H., Tsao, R., Yang, R. &amp; Cui, S.W. 2006. Phenolic acid profiles and antioxidant activities of wheat bran extracts and the effect of hydrolysis conditions. Food Chemistry 95: 466-473.</span></span></span>). Em cada tubo adicionou-se 0,2 mL de cada extrato nas concentrações (0,62; 0,31 e 0,15 mg mL<sup>-1</sup>) com 1 mL do reagente Folin-Ciocalteau agitado por 2 minutos e adicionado 0,8 mL de carbonato de sódio (Na<sub>2</sub>CO<sub>3</sub>) 7,5% (m/v). Para o tubo controle foi utilizado 1 mL do reagente Folin- Ciocalteau com 0,8 mL de Na<sub>2</sub>CO<sub>3</sub> e 0,2 mL de etanol, em triplicata. Os tubos foram deixados em banho-maria a 37 ̊C por 30 minutos na ausência de luz. Logo em seguida, foi realizado a leitura dos tubos em comprimento de onda de 765 nm. O teor de fenóis foi calculado e expresso em mg de equivalente de ácido gálico por grama de extrato (EAG.g<sup>-1</sup>), com base numa curva padrão preparada com ácido gálico. Todos os testes foram realizados em triplicata.</p>
+<p>Atividade antioxidante - A atividade antioxidante dos extratos foi determinada pelo método de redução do radical 2,2’-difenil-1-picril-hidrazil (DPPH), segundo a metodologia modificada por <span class="ref"><strong class="xref xrefblue">Brand-Williams <i>et al.</i> (1995</strong><span class="refCtt closed"><span>Brand-Williams, W., Cuvelier, M.E. &amp; Berset, C.L.W.T. 1995. Use of a free radical method to evaluate antioxidant activity. LWT-Food Science and Technology 1: 25-30.</span></span></span>), <span class="ref"><strong class="xref xrefblue">Sanchez-Moreno <i>et al</i>. (1998</strong><span class="refCtt closed"><span>Sánchez‐Moreno, C., Larrauri, J.A. &amp; Saura‐Calixto, F. 1998. A procedure to measure the antiradical efficiency of polyphenols. Journal of the Science of Food and Agriculture 76: 270-276.</span></span></span>). Foram preparadas soluções etanólicas das amostras nas concentrações de 5,0; 2,5; 1,25; 0,62; 0,31 e 0,15 mg mL<sup>-1</sup>. Foram utilizados 100 µL dos extratos com 2,4 mL de DPPH (0,04 mg mL<sup>-1</sup>). Para o tubo controle foram utilizados 100 µL de etanol com 2,4 mL de DPPH em triplicata. O meio reacional ficou por 30 minutos na ausência da luz, e posteriormente foi realizada a leitura em comprimento de onda 515 nm. A atividade sequestradora do radical DPPH pelos extratos nas diferentes concentrações foi calculada pela expressão do índice de varredura em porcentagem (IV%): IV% = (Abs <sub>DPPH</sub> - Abs <sub>Amostra</sub> / Abs <sub>DPPH</sub>) x 100. A concentração efetiva para inibir 50% do radical livre DPPH (CE<sub>50</sub>) foi obtida com auxílio do Software Excel 2019, onde, a partir dos valores das concentrações finais da amostra e o índice de varredura (IV%), foram originados gráficos de dispersão cujas equações das retas foram utilizadas para se obter os valores da média e desvio padrão. Para fins de comparação, foi construída uma curva de calibração com diferentes porcentagens do flavonoide quercetina, que apresenta elevada atividade antioxidante em radical livre DPPH.</p>
+<p>Avaliação da atividade anticolinesterásica <i>in vitro</i> - O ensaio para verificação da inibição da enzima acetilcolinesterase (AChE) dos extratos foi realizado de acordo com a metodologia descrita por <span class="ref"><strong class="xref xrefblue">Ellman <i>et al.</i> (1961</strong><span class="refCtt closed"><span>Ellman, G.L., Courtney, K.D., Andres Jr, V. &amp; Featherstone, R.M. 1961. A new and rapid colorimetric determination of acetylcholinesterase activity. Biochemical Pharmacology: 7: 88-95.</span></span></span>). Em placas estéreis de 96 poços, foram adicionados 25 µL de iodeto de acetiltiocolina (15 mM), 125 µL de 5,5’-ditiobis-[2-nitrobenzóico] na solução Tris/HCL (50 nM, pH 8, com 0,1 M de NaCL e 0,02 M de MgCL<sub>2</sub> .6H<sub>2</sub>O. (3 mM, DTNB ou reagente de Ellman)), 50 µL da solução Tris/HCL (50 nM, pH 8, com 0,1% de albumina sérica bovina (BSA) e 25 µL dos extratos de <i>Senna</i> spp. na concentraçao de 0,2 mg.mL<sup>-1</sup> em tampão Tris/HCL (50 mM, pH 8) de 0,2 mg.mL<sup>-1</sup> (<span class="ref"><strong class="xref xrefblue">Rhee <i>et al.</i> 2001</strong><span class="refCtt closed"><span>Rhee, I.K., van de Meent, M., Ingkaninan, K. &amp; Verpoorte, R. 2001. Screening for acetylcholinesterase inhibitors from Amaryllidaceae using silica gel thin-layer chromatography in combination with bioactivity staining. Journal of Chromatography A 915: 217-223.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Trevisan <i>et al.</i> 2003</strong><span class="refCtt closed"><span>Trevisan, M.T.S., Macedo, F.V.V., Meent, M.V.D., Rhee, I.K. &amp; Verpoorte, R. 2003. Seleção de plantas com atividade anticolinesterase para tratamento da doença de Alzheimer. Química Nova 26: 301-304.</span></span></span>). </p>
+<p>A absorbância foi aferida a 405 nm durante 30 segundos. Em seguida, foram adicionados 25 µL da enzima acetilcolinesterase (0,25 U.mL<sup>-1</sup>) e a absorbância foi aferida por minuto até o total de 25 minutos de incubação da enzima. Como padrão negativo foram utilizadas todas as soluções, excetuando-se a amostra. O padrão utilizado como controle positivo foi a fisostigmina (0,22 mg.mL<sup>-1</sup>.) e todas as amostras foram analisadas em triplicata. A atividade anticolinesterásica dos extratos vegetais foi determinada de acordo com os valores de CI<sub>50</sub> (Concentração inibitória capaz de inibir 50% da enzima acetilcolinesterase) como: alta potência (CI<sub>50</sub> &lt; 20 μg. mL<sup>-1</sup>); potência moderada (20 &lt; CI<sub>50</sub> &lt; 200 μg.mL<sup>-1</sup>) e baixa potência (200 &lt; CI<sub>50</sub> &lt; 1000 μg.mL<sup>-1</sup>) (<span class="ref"><strong class="xref xrefblue">Santos <i>et al</i>. 2018</strong><span class="refCtt closed"><span>Santos, G.H.F., Amaral, A. &amp; Da Silva, E.B. 2018. Antibacterial activity of irradiated extracts of Anacardium occidentale L. on multiresistant strains of Staphylococcus aureus. Applied Radiation and Isotopes 140: 327-332.</span></span></span>).</p>
+<p>Ensaio antifúngico <i>in vitro</i> - No ensaio para verificação da concentração inibitória mínima (CIM) dos EE das espécies de <i>Senna</i>, foram utilizadas cepas de <i>Trichophyton rubrum</i> obtidas a partir da micoteca da Universidade Federal de Pernambuco e do Centro Especializado de Micologia Médica (CEMM) da Universidade Federal do Ceará<i>.</i> Para este ensaio foi utilizado o método de microdiluição em caldo<i>,</i> de acordo com a metodologia descrita por (<span class="ref"><strong class="xref xrefblue">Neves <i>et al.</i> 2019</strong><span class="refCtt closed"><span>Neves, A.M., Silva, H.S., Souza, E.B., Fontenelle, R.O.S., Silva, A.C.S., Morais, S.M. 2019. Perfil fitoquímico e avaliação da atividade antifúngica da fração hexânica de Mitracarpus baturitensis (Rubiaceae). Essentia 20: 96-101. </span></span></span>) com as normas do protocolo <span class="ref"><strong class="xref xrefblue">Clinical Laboratory Standards Insitute do documento M38-A (CLSI M38-A2, 2008</strong><span class="refCtt closed"><span>Clinical and Laboratory Standards Institute. 2008. Reference Method for Broth Dilution Antifungal Susceptibility Testing of Filamentous Fungi (Approved Standard Document M38. CLSI), vol. M38-A2, Second ed. Clinical and Laboratory Standards Institute, Wayne, PA.</span></span></span>)<i>.</i> Em placas de 96 poços estéreis, foram adicionados 100 µL de meio RPMI em todos os poços e 10 mg mL<sup>-1</sup> dos extratos de <i>Senna</i> spp. foi acrescentado a todos os poços da primeira coluna e, em sequência foram efetuadas as diluições seriadas. Finalmente, 100 µL do inóculo foi adicionado aos poços da placa. Como controle foi utilizado o Cetoconazol (Sigma, Chemical Co., USA). Para as análises de susceptibilidade, os extratos etanólicos foram testados em concentrações variando de 0,002 a 2,5 mg mL<sup>-1</sup>. As placas foram cobertas com parafilme e incubadas a 37 °C e a leitura visual foi realizada após cinco dias para <i>T. rubrum</i>. Procedimento realizado em duplicata. A CIM é definida como a menor concentração do extrato capaz de inibir 100% do crescimento fúngico visível (<span class="ref"><strong class="xref xrefblue">Fontenelle <i>et al.</i> 2007</strong><span class="refCtt closed"><span>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Kerntopf, M.R., Brilhante, R.S.N., Cordeiro, R.A., Tomé, A.R., Queiroz, M.G.R., Nascimento, N.R.F. &amp; Sidrim, J.J.C. 2007. Chemical composition, toxicological aspects and antifungal activity of essential oil from Lippia sidoides Cham. Journal of Antimicrobial Chemotherapy 59: 934-940. </span></span></span>). A concentração fungicida mínima (CFM) foi determinada por subcultura de 100 μL da solução de poços sem turbidez no meio Ágar Dextrose de Batata, a 28 °C. (<span class="ref"><strong class="xref xrefblue">Fontenelle <i>et al.</i> 2008</strong><span class="refCtt closed"><span>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Brilhante, R.S.N., Cordeiro, R.A., Nascimento, N.R.F., Kerntopf, M.R., Sidrim, J.J.C. &amp; Rocha, M.F.G. 2008. Antifungal activity of essential oils of Croton species from the Brazilian caatinga biome. Journal of Applied Microbiology 104: 1383-1390.</span></span></span>).</p>
+<p>Análise estatística - Todas as determinações foram realizadas em triplicata e todos os resultados foram apresentados como média ± desvio-padrão (DP). Foram realizadas análises de variância (ANOVA) com duas repetições e o Teste Tukey, ao nível de significância de 5%, usando programa Graph Pad Prism<sup>®</sup> v5.01 (GraphPadSoftware, San Diego, CA, E.U.A.). As diferenças entre as médias foram consideradas significativas quando o valor obtido para "<i>p</i>" foi menor que 0,05 (<i>p</i> &lt; 0,05). </p>
+<p>Para análises da correlação entre os dados, foi utilizado o coeficiente de correlação de Pearson no software Microsoft Excel 2019, a qual mede o grau da correlação linear entre duas variáveis quantitativas. A intensidade dessa correlação é dada pelo “r”, que é um índice adimensional com valores situados entre -1,0 e 1,0. Quando o valor de r estiver entre 0,00-0,19 a correlação é muito fraca; entre 0,20-0,39 é fraca; 0,40-0,59 é uma correlação moderada; entre 0,60-0,79 é forte e finalmente entre 0,80-1,0 diz-se que é uma correlação muito forte (<span class="ref"><strong class="xref xrefblue">Mukaka 2012</strong><span class="refCtt closed"><span>Mukaka, M.M. 2012. Statistics corner: A guide to appropriate use of correlation coefficient in medical research. Malawi Med J. 24:69-71.</span></span></span>).</p>
+<h1 class="articleSectionTitle">Resultados e discussão<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>
+</h1>
+<p>Os fito-constituintes ou fitoquímicos são compostos químicos que desempenham importantes funções nas plantas. A triagem fitoquímica em materiais vegetais é geralmente o ponto de partida para o isolamento e purificação de compostos naturais com bioatividade (<span class="ref"><strong class="xref xrefblue">Omoregie &amp; Oikeh 2015</strong><span class="refCtt closed"><span>Omoregie, E.S. &amp; Oikeh, E.I. 2015. Comparative studies on the phytochemical composition, phenolic content and antioxidant activities of methanol leaf extracts of Spondias mombin and Polyathia longifolia. Jordan Journal of Biological Sciences 147: 1-5.</span></span></span>). A triagem fitoquímica preliminar revelou a presença de fenóis, taninos, flavonoides e esteroides para todos os extratos estudados (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>Tabela 2</a>). Entretanto, a presença de saponinas foi constatada apenas no EEF e EEC de <i>S. alata</i> e no EEF de <i>S. trachypus</i>. Já os alcaloides foram encontrados exclusivamente no EEF de <i>S. alata</i> e nenhuma das espécies apresentou triterpenoides. </p>
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+<strong><strong>Tablela 2</strong></strong><br> Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.<br>
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+<p>Os metabólitos detectados nas espécies estudadas são consistentes com os metabólitos descritos na literatura para o gênero <i>Senna</i>, conhecido por apresentar flavonoides, alcaloides, taninos, esteroides e saponinas em sua composição (<span class="ref"><strong class="xref xrefblue">Onyegeme-Okerenta <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Onyegeme-Okerenta, B.M., Nwosu, T. &amp; Wegwu, M.O. 2017. Proximate and phytochemical composition of leaf extract of Senna alata (L) Roxb. Journal of Pharmacognosy and Phytochemistry 6: 320-326.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Ishaku <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Ishaku, G.A., Arabo, A.A., Bassey, E.E., Uwem, A.A.U.M. &amp; Godwin, E.U. 2016. Physicochemical characterization and antibacterial activity of Senna occidentalis Linn. Journal of Chemistryand Chemical Sciences 6: 9-18. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Sudi <i>et al</i>. 2011</strong><span class="refCtt closed"><span>Sudi, I.Y., Ksgbiya, D.M., Muluh, E.K. &amp; Clement, A. 2011. Nutritional and phytochemical screening of Senna obtusifolia indigenous to Mubi, Nigeria. Advances in Applied Science Research 2: 432-437.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bukar <i>et al.</i> 2009</strong><span class="refCtt closed"><span>Bukar, A., Mukhtar, M. &amp; HASSAN, A. 2009. Phytochemical screening and antibacterial activity of leaf extracts of Senna siamea (Lam) on Pseudomonas aeruginosa. Bayero Journal of Pure and Applied Sciences 1: 139-142. </span></span></span>). É possível perceber que na análise de prospecção química dos extratos houve uma variação de metabólitos secundários. Este fato pode estar atribuído a vários fatores, entre eles estão as diferentes condições ambientais, tais como clima, radiação solar, nutrição mineral, sazonalidade, ritmo circadiano, temperatura, disponibilidade hídrica, e também os tipos de solvente e a metodologia empregada no processo de extração, que podem interferir consideravelmente no conteúdo de praticamente todas as classes de metabólitos secundários (<span class="ref"><strong class="xref xrefblue">Gomes <i>et al</i>. 2016</strong><span class="refCtt closed"><span>Gomes, E.M.C., Pena, R.D.C.M. &amp; da Silva, S.S.S.M. 2016. Composição fitoquímica e ação fungicida de extratos brutos de Cinnamomum zeylanicum sobre Quambalaria eucalypti. Biota Amazônia. 6: 54-58.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bezerra <i>et al.</i> 2013</strong><span class="refCtt closed"><span>Bezerra, A.S., Nörnberg, J.L., Lima, F.O., Rosa, M.B.D. &amp; Carvalho, L.M.D. 2013. Parâmetros climáticos e variação de compostos fenólicos em cevada. Ciência Rural 9: 1546-1552.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gobbo-Neto &amp; Lopes 2007</strong><span class="refCtt closed"><span>Gobbo-Neto, L. &amp; Lopes, N.P. 2007. Plantas medicinais: Fatores de influência no conteúdo de metabólitos secundários. Química Nova 30: 374-381.</span></span></span>).</p>
+<p>Os teores de fenóis totais apresentaram diferenças significativas entre os extratos etanólicos das diferentes partes e espécies vegetais estudadas (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). O conteúdo de fenóis totais para os EEF variou de 32,60 ± 0,53 a 184,8 ± 5,09 EAG/g, enquanto que para o EEC foram de 30,03± 1,00 a 191,3 ± 0,47 EAG/g. Os maiores níveis de fenóis totais foram detectados na espécie <i>S. trachypus</i>. Os dados da literatura sobre o conteúdo de compostos fenólicos obtidos a partir do extrato aquoso, etanólico e acetona da raiz de <i>S. alata</i>, apresentaram uma concentração de fenóis de 46,3, 78,21 e 21,42 mg EAG/g, respectivamente, e de flavonoides de 26,17, 39,29 e 9,65 mg de equivalente de quercetina por grama de extrato (EQ/g), respectivamente (<span class="ref"><strong class="xref xrefblue">Ita &amp; Ndukwe 2017</strong><span class="refCtt closed"><span>Ita, B.N., &amp; Ndukwe, G.I. Antioxidant activity of Senna alata root extracts. 2017. J Nat Prod Resour 3: 94-96. </span></span></span>). Já o extrato etanólico preparado a partir das folhas de <i>S. obtusifolia</i> por <span class="ref"><strong class="xref xrefblue">Ali <i>et al</i>. (2019</strong><span class="refCtt closed"><span>Ali, I., Yisa, J. &amp; Jacob, J.O. 2019. Corrosion inhibitory potential of ethanol extract of Senna obtusifolia on Mild Steel in 5M HCl. Journal of Chemical Society of Nigeria 44: 187-198. </span></span></span>), apresentou um teor de fenóis e de flavonoides de 14,39 mg/g e 2,85 mg/g, respectivamente, demonstrando possuir teor de compostos fenólicos inferior ao das mostras de <i>S. obtusifolia</i> encontradas no presente estudo. Além disso, o conteúdo de polifenóis encontrado no extrato etanólico e nas frações obtidas a partir das folhas de <i>S. occidentalis</i> por <span class="ref"><strong class="xref xrefblue">Yakubu <i>et al.</i> (2018</strong><span class="refCtt closed"><span>Yakubu, O.E., Otitoju, O., Imarenezor, E.P.K., Tatah, S.V. &amp; Habibu, B. 2018. Fractionation and determination of antioxidant activities, of the Leaves of Senna Occidentalis ethanol extract. Pharmacology, 6: 26-30.</span></span></span>) variou de 139 mg/mL a 206 mg/mL e de flavonoides de 104 a 142 mg/mL. Já para os extratos preparados a partir das folhas e casca do caule de <i>S. siamea</i> revelaram um teor de fenóis totais de 10,21 ± 0,25 g/g e 24,77 ± 0,15 g/g, respectivamente. Por outro lado, o teor de flavonoides foi de 0,08 ± 0,01 g/g para as folhagens, e de 0,04 ± 0,01 g/g para a casca do caule (<span class="ref"><strong class="xref xrefblue">Kwada &amp; Tella 2009</strong><span class="refCtt closed"><span>Kwada, A.D. &amp; Tella, I.O. 2009. Determination of infochemicals and the phytochemical screening of the foliage and stem-bark of Senna siamea (lam.) in Yola, Adamawa State. Journal of Medicinal Plants Research 3: 630-640.</span></span></span>). Para os extratos etanólicos das folhas e raízes de <i>S. trachypus</i> o teor de fenóis totais encontrado foi de 322,09 ± 2,83 EAG/g e de 1277,34 ± 79,54 EAG/g, respectivamente (<span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>).<i>Senna</i>.</p>
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+<strong><strong>Table 3.</strong></strong><br> Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).<br>
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+</div>
+			</div>
+<p>Os resultados da atividade antioxidante dos extratos de <i>Senna</i> spp. mostraram que os valores de CE<sub>50</sub> para o EEF variaram de 0,63 ± 0,01 a 8,20 ± 0,07 µg/mL, sendo o EEF de <i>S. trachypus</i> o que apresentou menor CE<sub>50</sub> com atividade antirradicalar superior ao da quercetina e, portanto, maior potencial antioxidante (<span class="ref"><strong class="xref xrefblue">Villano <i>et al</i>. 2007</strong><span class="refCtt closed"><span>Villano, D., Fernandez-Pachón, M.S., Moya, M.L., Troncoso, A.M. &amp; García-Parrilla, M.C. 2007. Radical scavenging ability of polyphenolic compounds towards DPPH free radical. Talanta, 71: 230-235. </span></span></span>). Já para o EEC os valores de CE<sub>50</sub> variaram de 0,83 ± 0,01 a 11,19 ± 0,15 µg/mL (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). Foi observado que o EEC de <i>S. siamea</i> apresentou capacidade antirradicalar próximo à quercetina. Semelhantes aos nossos resultados, estudos anteriores revelaram que as espécies de <i>S. alata, S. obtusifolia, S. occidentalis, S. siamea</i> e <i>S. trachypus</i>, apresentaram potencial antioxidante e que esta atividade está atribuída à presença de compostos fenólicos (<span class="ref"><strong class="xref xrefblue">Coelho <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Coelho, E.M.P., Barbosa, M.C., Mito, M.S., Mantovanelli, G.C., Oliveira, R.S., &amp; Ishii-Iwamoto, E.L. 2017. The activity of the antioxidant defense system of the weed species Senna obtusifolia L. and its resistance to allelochemical stress. Journal of Chemical Ecology 7: 725-738.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Ita &amp; Ndukwe 2017</strong><span class="refCtt closed"><span>Ita, B.N., &amp; Ndukwe, G.I. Antioxidant activity of Senna alata root extracts. 2017. J Nat Prod Resour 3: 94-96. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Barnaby <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Barnaby, A.G., Reid, R. &amp; Warren, D. 2016. Antioxidant activity, total phenolics and fatty acid profile of Delonix regia, Cassia fistula, Spathodea campanulata, Senna siamea and Tibouchina granulosa. J Anal Pharm Res 3: 00056.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>). </p>
+<p>Os resultados obtidos na análise de inibição da enzima acetilcolinesterase foram comparados ao do alcaloide fisostigmina que foi o primeiro inibidor descoberto. Os experimentos de inibição da enzima acetilcolinesterase <i>in vitro</i> para as espécies de <i>Senna</i> produziram apenas resultados com potência moderada (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). Relatos confirmam a atividade antiacetilcolinesterásica de vários taninos isolados do fruto <i>Terminalia chebula</i> Retz.<i>,</i> (Combretaceae) que exibiram um efeito de inibição contra a enzima acetilcolinesterase <i>in vitro</i> (<span class="ref"><strong class="xref xrefblue">Kim <i>et al.</i> 2018</strong><span class="refCtt closed"><span>Kim, M.S., Lee, D.Y., Sung, S.H. &amp; Jeon, W.K. 2018. Anti-cholinesterase activities of hydrolysable tannins and polyhydroxytriterpenoid derivatives from Terminalia chebula Retz. fruit. Fruit Rec Nat Prod 12: 284-289.</span></span></span>). Outros compostos, como saponinas, alcaloides e compostos fenólicos, também são relatados na literatura como inibidores da enzima acetilcolinesterase (<span class="ref"><strong class="xref xrefblue">Paiva <i>et al</i>. 2021</strong><span class="refCtt closed"><span>Paiva, J.R., Queiroz, S.A.S., Pereira, R.D.C.A., Ribeiro, P.R.V., Alves, F.E.G., Silva, L.M.A., Zocolo, G.J., Brito, E.S., Alves, D.R., Morais, S.M., Tavares, J., Pinto, F.C.L., Andrade, G.M., Pessoa, O.D.L., &amp; Canuto, K.M. 2021. Chemical composition and anticholinesterase activity of cultivated bulbs from Hippeastrum elegans, a potential tropical source of bioactive alkaloids. Phytochemistry Letters 43: 27-34.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kozachok <i>et al</i>. 2020</strong><span class="refCtt closed"><span>Kozachok, S., Pecio, Ł., Orhan, I.E., Deniz, F.S.S., Marchyshyn, S., &amp; Oleszek, W. 2020. Reinvestigation of Herniaria glabra L. saponins and their biological activity. Phytochemistry 169: 112162.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Adedayo <i>et al</i>. 2015</strong><span class="refCtt closed"><span>Adedayo, B.C., Oboh, G., Oyeleye, S.I., Ejakpovi, I.I., Boligon, A.A., &amp; Athayde, M.L. 2015. Blanching alters the phenolic constituents and in vitro antioxidant and anticholinesterases properties of fireweed (Crassocephalum crepidioides). Journal of Taibah University Medical Sciences 10: 419-426.</span></span></span>). Estas classes de compostos foram detectadas na triagem fitoquímica, embora provavelmente as concentrações nos extratos eram muito baixas para dar resultados satisfatórios no ensaio. Os extratos foliares e do caule de <i>S. trachypus</i> apresentaram os valores mais satisfatórios de inibição da enzima acetilcolinesterase, indicando que o isolamento de metabólitos pode levar a potenciais agentes antiacetilcolinesterásicos. Na literatura, não foram encontrados estudos do potencial anticolinesterásico paras as espécies de <i>Senna</i> referenciadas, sendo este o primeiro relato de estudo de atividade de inibição para esta enzima. </p>
+<p>Para os extratos de <i>Senna</i> spp., foi observada forte correlação negativa entre os valores de fenóis totais e CE<sub>50</sub> (r = - 0,71), mostrando que quanto maior os teores de fenóis totais, menor a CE<sub>50</sub> e, consequentemente, maior o potencial antioxidante, uma vez que a CE<sub>50</sub> está inversamente relacionada à capacidade antioxidante de um composto (<span class="ref"><strong class="xref xrefblue">Villano <i>et al</i>. 2007</strong><span class="refCtt closed"><span>Villano, D., Fernandez-Pachón, M.S., Moya, M.L., Troncoso, A.M. &amp; García-Parrilla, M.C. 2007. Radical scavenging ability of polyphenolic compounds towards DPPH free radical. Talanta, 71: 230-235. </span></span></span>). Dentre os extratos analisados podemos observar na figura 1 o EEF de <i>S. trachypus.</i></p>
+<p>
+				<div class="row fig" id="">
+<a name=""></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf1.jpg" data-toggle="modal" data-target="#ModalFig"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf1.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Na correlação da atividade de inibição da enzima acetilcolinesterase, representada pelo CI<sub>50</sub> com teor de fenóis totais, observou-se uma correlação muito forte (r = -0,84) entre estas duas variáveis, evidenciando que ambas são inversamente proporcionais entre si, ou seja, à medida que o teor de fenóis totais aumenta o valor de CI<sub>50</sub> diminui, como pode ser observado para o EEF de <i>S. occidentalis</i> (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>Figura 2</a>). Isso demonstra que os compostos fenólicos podem ser determinantes nessa atividade, de modo que alguns estudos evidenciaram que flavonoides e outros compostos fenólicos possuem atividade anticolinesterásica (<span class="ref"><strong class="xref xrefblue">Amessis-Ouchemoukh <i>et al</i>. 2014</strong><span class="refCtt closed"><span>Amessis-Ouchemoukh, N., Madani, K., Falé, P.L., Serralheiro, M.L., Araújo, M.E.M. 2014. Antioxidant capacity and phenolic contents of some Mediterranean medicinal plants and their potential role in the inhibition of cyclooxygenase-1 and acetylcholinesterase activities. Industrial Crops and Products, 53: 6-15.</span></span></span>). </p>
+<p>
+				<div class="row fig" id="f2">
+<a name="f2"></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf2.jpg" data-toggle="modal" data-target="#ModalFigf2"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf2.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 2.</strong><br>Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Houve uma correlação moderada (r = 0,43) entre a CI<sub>50</sub> e a CE<sub>50</sub>. Analisando a <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>figura 3</a>, é possível perceber que o EEF e EEC de <i>S. alata</i> e EEF de <i>S. obtusifolia</i> se destacam no gráfico<i>,</i> o que sugere uma grande capacidade dos antioxidantes, como os compostos fenólicos, presentes nos extratos analisados, de atuarem não só através da inibição da acetilcolinesterase (AChEI) mas também por mecanismos de redução de radicais livres.</p>
+<p>
+				<div class="row fig" id="f3">
+<a name="f3"></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf3.jpg" data-toggle="modal" data-target="#ModalFigf3"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf3.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 3.</strong><br>Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Os extratos etanólicos das folhas e caule de <i>S. alata, S. obtusifolia, S. occidentalis</i> e <i>S. siamea,</i> apresentaram efeito inibitório contra algumas cepas de <i>T. rubrum</i>. A maioria dos extratos foram eficazes em diferentes concentrações, com CIM que variaram de 0,07 mg/mL à 2,5 mg/mL e CFM de 0,15 a 5,0 mg/mL contra a grande maioria das cepas fúngicas testadas. Dentre os extratos testados, os de <i>S. trachypus</i> foram eficazes contra todas as cepas de <i>T. rubrum</i> com CIM que variaram de 0,31 a 0,62 mg/mL e o CFM de 0,62 a 1,25 mg/mL, para ambos os extratos (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>Tabela 4</a>). A presença de compostos fitoquímicos tem sido associada às atividades antimicrobianas da maioria dos materiais vegetais. Algumas classes de metabólitos foram identificadas nesse estudo e podem ser associadas à atividade antimicrobiana (<span class="ref"><strong class="xref xrefblue">Santos <i>et al.</i> 2018</strong><span class="refCtt closed"><span>Santos, T.C.D., Gomes, T.M., Pinto, B.A.S., Camara, A.L. &amp; Paes, A.M.D.A. 2018. Naturally occurring acetylcholinesterase inhibitors and their potential use for Alzheimer's disease therapy. Frontiers in Pharmacology 9: 1192.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>). </p>
+<div>
+				<div class="row table" id="t4">
+<a name="t4"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 4. </strong></strong><br> Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.<br>
+</div>
+</div>
+			</div>
+<p>Estudos anteriores realizados com o extrato etanólico da casca do caule de <i>S. alata</i> contra fungos dermatofíticos, entre eles espécies de <i>Trychophyton,</i> revelou um CIM de 5,0 mg/mL para todos os dermatófitos testados (<span class="ref"><strong class="xref xrefblue">Sule <i>et al.</i> 2011</strong><span class="refCtt closed"><span>Sule, W.F., Okonko, I.O., Omo-Ogun, S., Nwanze, J.C., Ojezele, M.O., Ojezele, O.J., Alli, J.A., Soyemi, E.T. &amp; Olaonipekun, T.O. 2011. Phytochemical properties and in-vitro antifungal activity of Senna alata Linn. crude stem bark extract. Journal of Medicinal Plants Research, 5: 176-183.</span></span></span>). A capacidade antifúngica de extratos de diferentes polaridades preparados a partir das folhas de <i>S. obtusifolia</i> apresentaram um CIM que variou de 500 a 2000 µg/mL contra diferentes espécies de fungos filamentosos (<span class="ref"><strong class="xref xrefblue">Doughari <i>et al.</i> 2008</strong><span class="refCtt closed"><span>Doughari, J.H., El-mahmood, A.M. &amp; Tyoyina, I. 2008. Antimicrobial activity of leaf extracts of Senna obtusifolia (L). African Journal of Pharmacy and Pharmacology 2: 7-13.</span></span></span>). Os resultados obtidos de extratos foliares de polaridades diferentes de <i>S. occidentalis</i> revelaram que o extrato metanólico mostrou maior atividade antifúngica entre os demais extratos testados, em uma concentração inibitória mínima de 25 mg/mL (<span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>). Testes utilizando extratos preparados com solventes de diferentes polaridades a partir das folhas de <i>S. siamea</i> apresentaram CIM que variaram de 0,032 a 0,128 mg/mL contra o fungo <i>Cryptococcus gattii</i> (<span class="ref"><strong class="xref xrefblue">Nnadi <i>et al.</i> 2019</strong><span class="refCtt closed"><span>Nnadi, N.E., Anukam, N.C., Ayika, P.D., Rotdung, K., Gokum, S.S., Ayanbimpe, G.M., Nvau, J. &amp; Enweani, I. 2019. The in Vitro antifungal activity of some Nigeria medicinal plants against Cryptococcus gattii. IOSR Journal of Pharmacy 9: 16-24. </span></span></span>). Na literatura, não foram encontrados estudos do potencial antifúngico para a espécie de <i>S. trachypus</i>, sendo este o primeiro registro de atividade antifúngica para a referida espécie. </p>
+<p>Pesquisas têm revelado que o potencial antifúngico de extratos vegetais está intimamente relacionado, entre outros fatores, com as suas variações quantitativas de compostos fenólicos, dentre eles os flavonoides. Nosso estudo confirmou que as espécies estudadas possuem propriedades antifúngicas, e que seus efeitos sobre os dermatófitos fundamentam-se em seus teores de compostos fenólicos encontrados, e os demais outros metabólitos secundários aqui não estudados. Os efeitos antifúngicos atribuídos aos compostos fenólicos podem resultar na ruptura da membrana celular, ou ainda, inibir a divisão celular e o desenvolvimento das hifas por meio de genes específicos, além de interferir nas vias metabólicas e/ou induzir a apoptose por perturbar a homeostase redox (<span class="ref"><strong class="xref xrefblue">Lagrouh <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Lagrouh, F., Dakka, N. &amp; Bakri, Y. 2017.The antifungal activity of Moroccan plants and the mechanism of action of secondary metabolites from plants. Journal de Mycologie Medicale 27: 303-311.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Mohamed <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Mohamed, M.S., Saleh, A.M., Abdel-Farid, I.B. &amp; El-Naggar, S.A. 2017. Growth, hydrolases and ultrastructure of Fusarium oxysporum as affected by phenolic rich extracts from several xerophytic plants. Pesticide Biochemistry and Physiology 141: 57-64. </span></span></span>).</p>
+<p>Foram detectados, nos EEF e EEC das espécies de <i>Senna</i>, a presença de metabólitos secundários, alto teor de fenóis totais e capacidade antioxidante para todas as espécies, em especial <i>S. trachypus</i>. Para a atividade anticolinesterase apenas a espécie de <i>S. trachypus</i> manifestou uma melhor ação inibitória. Nas condições experimentais utilizadas, evidenciou-se atividade antifúngica das espécies frente a maioria dos dermatófitos testados, em especial os extratos de <i>S. trachypus</i>. Foi observada também correlação forte, muito forte e moderada entre as variáveis fenóis totais e atividade antioxidante, fenóis totais e antiacetilcolinesterase e atividade antioxidante e antiacetilcolinesterase, respectivamente<i>.</i> Os resultados apontam que <i>S. trachypus</i>, espécie endêmica da Caatinga, é a mais promissora entre todas as plantas estudadas, representando uma fonte potencial para a obtenção de compostos químicos úteis para estudos clínicos e farmacológicos, visando o desenvolvimento de novos agentes farmacológicos naturais. </p>
+</div>
+<div class="articleSection" data-anchor="Agradecimentos">
+<h1 class="articleSectionTitle">Agradecimentos</h1>
+<p>Os autores agradecem a Universidade Estadual do Ceará (UECE) e a Universidade Estadual Vale do Acaraú (UVA) pelo apoio técnico, e a Fundação Cearense de Apoio ao Desenvolvimento Científico e Tecnológico (FUNCAP) pelo apoio financeiro concedido (processos PBI3-0139-00252.01.00/18; BP4-0172-00170.01.00/20). </p>
+</div>
+<div class="articleSection" data-anchor="Literatura citada">
+<h1 class="articleSectionTitle">Literatura citada</h1>
+<div class="ref-list"><ul class="refList">
+<li><div>Ali, I., Yisa, J. &amp; Jacob, J.O. 2019. Corrosion inhibitory potential of ethanol extract of <i>Senna obtusifolia</i> on Mild Steel in 5M HCl. Journal of Chemical Society of Nigeria 44: 187-198. </div></li>
+<li><div>Adedayo, B.C., Oboh, G., Oyeleye, S.I., Ejakpovi, I.I., Boligon, A.A., &amp; Athayde, M.L. 2015. Blanching alters the phenolic constituents and <i>in vitro</i> antioxidant and anticholinesterases properties of fireweed (<i>Crassocephalum crepidioides</i>). Journal of Taibah University Medical Sciences 10: 419-426.</div></li>
+<li><div>Amessis-Ouchemoukh, N., Madani, K., Falé, P.L., Serralheiro, M.L., Araújo, M.E.M. 2014. Antioxidant capacity and phenolic contents of some Mediterranean medicinal plants and their potential role in the inhibition of cyclooxygenase-1 and acetylcholinesterase activities. Industrial Crops and Products, 53: 6-15.</div></li>
+<li><div>Bardakci, H., CeleP, E., Gözet, T., Kan, Y. &amp; Kirmizibekmez, H. 2019. Phytochemical characterization and antioxidant activities of the fruit extracts of several <i>Crataegus taxa</i> South African Journal of Botany 124: 5-13. </div></li>
+<li><div>Barnaby, A.G., Reid, R. &amp; Warren, D. 2016. Antioxidant activity, total phenolics and fatty acid profile of <i>Delonix regia</i>, <i>Cassia fistula</i>, <i>Spathodea campanulata</i>, <i>Senna siamea</i> and <i>Tibouchina granulosa</i> J Anal Pharm Res 3: 00056.</div></li>
+<li><div>Bezerra, A.S., Nörnberg, J.L., Lima, F.O., Rosa, M.B.D. &amp; Carvalho, L.M.D. 2013. Parâmetros climáticos e variação de compostos fenólicos em cevada. Ciência Rural 9: 1546-1552.</div></li>
+<li><div>BFG. 2018. Brazilian Flora 2020: Innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 1513-1527. </div></li>
+<li><div>Bieski, I.G.C., Leonti, M., Arnason, J.T., Ferrier, J., Rapinski, M., Violante, I.M.P., Balogun,S.O., Pereira, J.F.C.A., Figueiredo, R.D.C.F., Lopes, C.R.A.S., Silva, D.R.D., Pacini, A., Albuquerque, U.P. &amp; Martins, D.T.D.O. 2015. Ethnobotanical study of medicinal plants by population of valley of Juruena region, legal amazon, Mato Grosso, Brazil. Journal of Ethnopharmacology 173: 383-423.</div></li>
+<li><div>Brand-Williams, W., Cuvelier, M.E. &amp; Berset, C.L.W.T. 1995. Use of a free radical method to evaluate antioxidant activity. <i>LWT</i>-Food Science and Technology 1: 25-30.</div></li>
+<li><div>Bukar, A., Mukhtar, M. &amp; HASSAN, A. 2009. Phytochemical screening and antibacterial activity of leaf extracts of <i>Senna siamea</i> (Lam) on <i>Pseudomonas aeruginosa</i> Bayero Journal of Pure and Applied Sciences 1: 139-142. </div></li>
+<li><div>Coelho, E.M.P., Barbosa, M.C., Mito, M.S., Mantovanelli, G.C., Oliveira, R.S., &amp; Ishii-Iwamoto, E.L. 2017. The activity of the antioxidant defense system of the weed species <i>Senna obtusifolia</i> L. and its resistance to allelochemical stress. Journal of Chemical Ecology 7: 725-738.</div></li>
+<li><div>Clinical and Laboratory Standards Institute. 2008. Reference Method for Broth Dilution Antifungal Susceptibility Testing of Filamentous Fungi (Approved Standard Document M38. CLSI), vol. M38-A2, Second ed. Clinical and Laboratory Standards Institute, Wayne, PA.</div></li>
+<li><div>Doughari, J.H., El-mahmood, A.M. &amp; Tyoyina, I. 2008. Antimicrobial activity of leaf extracts of <i>Senna obtusifolia</i> (L). African Journal of Pharmacy and Pharmacology 2: 7-13.</div></li>
+<li><div>Ellman, G.L., Courtney, K.D., Andres Jr, V. &amp; Featherstone, R.M. 1961. A new and rapid colorimetric determination of acetylcholinesterase activity. Biochemical Pharmacology: 7: 88-95.</div></li>
+<li><div>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Brilhante, R.S.N., Cordeiro, R.A., Nascimento, N.R.F., Kerntopf, M.R., Sidrim, J.J.C. &amp; Rocha, M.F.G. 2008. Antifungal activity of essential oils of <i>Croton</i> species from the Brazilian caatinga biome. Journal of Applied Microbiology 104: 1383-1390.</div></li>
+<li><div>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Kerntopf, M.R., Brilhante, R.S.N., Cordeiro, R.A., Tomé, A.R., Queiroz, M.G.R., Nascimento, N.R.F. &amp; Sidrim, J.J.C. 2007. Chemical composition, toxicological aspects and antifungal activity of essential oil from <i>Lippia sidoides</i> Cham. Journal of Antimicrobial Chemotherapy 59: 934-940. </div></li>
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+<li><div>Ishaku, G.A., Arabo, A.A., Bassey, E.E., Uwem, A.A.U.M. &amp; Godwin, E.U. 2016. Physicochemical characterization and antibacterial activity of <i>Senna occidentalis</i> Linn. Journal of Chemistryand Chemical Sciences 6: 9-18. </div></li>
+<li><div>Ita, B.N., &amp; Ndukwe, G.I. Antioxidant activity of <i>Senna alata</i> root extracts. 2017. J Nat Prod Resour 3: 94-96. </div></li>
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+<li><div>Kwada, A.D. &amp; Tella, I.O. 2009. Determination of infochemicals and the phytochemical screening of the foliage and stem-bark of <i>Senna siamea</i> (lam.) in Yola, Adamawa State. Journal of Medicinal Plants Research 3: 630-640.</div></li>
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+<li><div>Mohamed, M.S., Saleh, A.M., Abdel-Farid, I.B. &amp; El-Naggar, S.A. 2017. Growth, hydrolases and ultrastructure of <i>Fusarium oxysporum</i> as affected by phenolic rich extracts from several xerophytic plants. Pesticide Biochemistry and Physiology 141: 57-64. </div></li>
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+<li><div>Neves, A.M., Costa, O.S., Coutinho, M.G.S., Souza, E.B., Santos, H.S., Silva, M.G.V. &amp; Fontenelle, R.O.S. 2017. Caracterização química e o potencial antimicrobiano de espécies do gênero <i>Senna</i> Mill (Fabaceae). Rev. Virtual Quim 9: 2506-2538.</div></li>
+<li><div>Neagu, E., Radu, G.L., Albu, C., &amp; Paun, G. 2016. Antioxidant activity, acetylcholinesterase and tyrosinase inhibitory potential of <i>Pulmonaria officinalis</i> and <i>Centarium umbellatum</i> extracts. Saudi Journal of Biological Sciences, 3: 578-585.</div></li>
+<li><div>Nnadi, N.E., Anukam, N.C., Ayika, P.D., Rotdung, K., Gokum, S.S., Ayanbimpe, G.M., Nvau, J. &amp; Enweani, I. 2019. The <i>in Vitro</i> antifungal activity of some Nigeria medicinal plants against <i>Cryptococcus gattii</i> IOSR Journal of Pharmacy 9: 16-24. </div></li>
+<li><div>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of <i>Senna occidentalis</i> (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</div></li>
+<li><div>Onyegeme-Okerenta, B.M., Nwosu, T. &amp; Wegwu, M.O. 2017. Proximate and phytochemical composition of leaf extract of <i>Senna alata</i> (L) Roxb. Journal of Pharmacognosy and Phytochemistry 6: 320-326.</div></li>
+<li><div>Omoregie, E.S. &amp; Oikeh, E.I. 2015. Comparative studies on the phytochemical composition, phenolic content and antioxidant activities of methanol leaf extracts of <i>Spondias mombin</i> and <i>Polyathia longifolia</i> Jordan Journal of Biological Sciences 147: 1-5.</div></li>
+<li><div>Paiva, J.R., Queiroz, S.A.S., Pereira, R.D.C.A., Ribeiro, P.R.V., Alves, F.E.G., Silva, L.M.A., Zocolo, G.J., Brito, E.S., Alves, D.R., Morais, S.M., Tavares, J., Pinto, F.C.L., Andrade, G.M., Pessoa, O.D.L., &amp; Canuto, K.M. 2021. Chemical composition and anticholinesterase activity of cultivated bulbs from <i>Hippeastrum elegans</i>, a potential tropical source of bioactive alkaloids. Phytochemistry Letters 43: 27-34.</div></li>
+<li><div>Pellerin, R.J., Waminal, N.E. &amp; Kim, H.H. 2019. FISH mapping of rDNA and telomeric repeats in 10 <i>Senna</i> species. Horticulture, Environment, and Biotechnology 60: 253-260.</div></li>
+<li><div>Penido, A.B., De Morais, S.M., Ribeiro, A.B., Alves, D.R., Rodrigues, A.L.M., dos Santos, L.H. &amp; de Menezes, J.E.S.A. 2017. Medicinal plants from northeastern Brazil against Alzheimer’s disease. Evidence-Based Complementary and Alternative Medicine 2017: 1-7. </div></li>
+<li><div>Queiroz, L.P. 2009. Leguminosas da Caatinga. Universidade Estadual de Feira de Santana, Feira de Santana, 467 p.</div></li>
+<li><div>Rhee, I.K., van de Meent, M., Ingkaninan, K. &amp; Verpoorte, R. 2001. Screening for acetylcholinesterase inhibitors from Amaryllidaceae using silica gel thin-layer chromatography in combination with bioactivity staining. Journal of Chromatography A 915: 217-223.</div></li>
+<li><div>Rodrigues, F.C., Dos Santos, A.T.L., Machado, A.J.T., Bezerra, C.F., de Freitas, T.S., Coutinho, H.D.M., Morais-Braga, M.F.B., Bezerra, J.W.A., Duarte, A.E., Kamdem, J.P., Boligon, A.A., Campos, M.M.A., Barros, L.M. 2019. Chemical composition and anti-<i>Candida</i> potencial of the extracts of <i>Tarenaya spinosa</i> (Jacq.) Raf.(Cleomaceae). Comparative immunology, microbiology and infectious diseases 64: 14-19.</div></li>
+<li><div>Santos, G.H.F., Amaral, A. &amp; Da Silva, E.B. 2018. Antibacterial activity of irradiated extracts of <i>Anacardium occidentale</i> L. on multiresistant strains of <i>Staphylococcus aureus</i> Applied Radiation and Isotopes 140: 327-332.</div></li>
+<li><div>Santos, T.C.D., Gomes, T.M., Pinto, B.A.S., Camara, A.L. &amp; Paes, A.M.D.A. 2018. Naturally occurring acetylcholinesterase inhibitors and their potential use for Alzheimer's disease therapy. Frontiers in Pharmacology 9: 1192.</div></li>
+<li><div>Sánchez‐Moreno, C., Larrauri, J.A. &amp; Saura‐Calixto, F. 1998. A procedure to measure the antiradical efficiency of polyphenols. Journal of the Science of Food and Agriculture 76: 270-276.</div></li>
+<li><div>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of <i>Senna</i> Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</div></li>
+<li><div>Souza, V.C.; Bortoluzzi, R.L.C. 2015. <i>Senna</i> in Lista de Espécies da Flora do Brasil. Jardim Botânico do Rio de Janeiro. </div></li>
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+<li><div>Yakubu, O.E., Otitoju, O., Imarenezor, E.P.K., Tatah, S.V. &amp; Habibu, B. 2018. Fractionation and determination of antioxidant activities, of the Leaves of <i>Senna Occidentalis</i> ethanol extract. Pharmacology, 6: 26-30.</div></li>
+</ul></div>
+</div>
+<div class="articleSection" data-anchor="Datas de Publicação ">
+<h1 class="articleSectionTitle">Datas de Publicação </h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Publicação nesta coleção</strong><br>21 Fev 2022</li>
+<li>
+<strong>Data do Fascículo</strong><br>2022</li>
+</ul></div></div>
+</div>
+<div class="articleSection" data-anchor="Histórico">
+<h1 class="articleSectionTitle">Histórico</h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Recebido</strong><br>14 Out 2020</li>
+<li>
+<strong>Aceito</strong><br>03 Dez 2021</li>
+</ul></div></div>
+</div>
+<section class="documentLicense"><div class="container-license"><div class="row">
+<div class="col-sm-3 col-md-2"><a href="https://creativecommons.org/licenses/by/4.0/" target="_blank" title=""><img src="https://licensebuttons.net/l/by/4.0//88x31.png" alt="Creative Common - by 4.0 "></a></div>
+<div class="col-sm-9 col-md-10"><a href="https://creativecommons.org/licenses/by/4.0/" target="_blank" title="">Este é um artigo publicado em acesso aberto sob uma licença Creative Commons</a></div>
+</div></div></section></article>
+</div>
+</div></div></section><div class="modal fade ModalDefault ModalTutors" id="ModalTutors" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Sobre os autores</h4>
+</div>
+<div class="modal-body">
+<div class="info">
+<div class="tutors">
+<strong> Andréa Maria Neves </strong><strong>4</strong><br><div> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-7388-1844" class="btnContribLinks orcid">http://orcid.org/0000-0002-7388-1844</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Selene Maia de Morais </strong><br><div> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2766-3790" class="btnContribLinks orcid">http://orcid.org/0000-0002-2766-3790</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Hélcio Silva dos Santos </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Exatas e Tecnologia, Curso de Química, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0001-5527-164X" class="btnContribLinks orcid">http://orcid.org/0000-0001-5527-164X</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Marcílio Matos Ferreira </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0003-2503-9772" class="btnContribLinks orcid">http://orcid.org/0000-0003-2503-9772</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Ricardo Carneiro Vera Cruz </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2035-0425" class="btnContribLinks orcid">http://orcid.org/0000-0002-2035-0425</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Elnatan Bezerra de Souza </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-5222-4378" class="btnContribLinks orcid">http://orcid.org/0000-0002-5222-4378</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Lúcia Betânia da Silva Andrade </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-4384-5738" class="btnContribLinks orcid">http://orcid.org/0000-0002-4384-5738</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Raquel Oliveira dos Santos Fontenelle </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-8865-5954" class="btnContribLinks orcid">http://orcid.org/0000-0002-8865-5954</a></li></ul>
+<div class="clearfix"></div>
+</div>
+</div>
+<div class="info">
+					<h3><sup>4</sup></h3> Autor para correspondência: <a href="mailto:andreamarianeves@gmail.com">andreamarianeves@gmail.com</a>
+				</div>
+<div class="info">
+<h3>Editora Associada:</h3>
+<div> Catarina Carvalho Nievola</div>
+</div>
+<div class="info">
+<h3>Contribuição dos autores</h3>
+<div>
+<b>Andréa Maria Neves:</b> Contribuição substancial em todas as etapas da pesquisa e para a confecção do manuscrito. <b>Selene Maia de Morais:</b> Contribuição na realização do teste de acetilcolinesterase; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Hélcio Silva dos Santos:</b> Contribuição na preparação dos extratos; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Marcílio Matos Ferreira:</b> Contribuição para a coleta das espécies e preparação dos extratos. <b>Ricardo Carneiro Vera Cruz:</b> Contribuição na realização dos testes fitoquímicos e quantificação de fenóis totais. <b>Elnatan Bezerra de Souza:</b> Contribuição na coleta e identificação das espécies; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Lúcia Betânia da Silva Andrade:</b> Contribuição na realização da atividade antioxidante, para a interpretação dos dados, e para revisão crítica, agregando conteúdo intelectual. <b>Raquel Oliveira dos Santos Fontenelle:</b> Contribuição nos testes antifúngicos e para revisão crítica, agregando conteúdo intelectual. </div>
+</div>
+<div class="info">
+<h3>Conflitos de interesse</h3>
+<div> Os autores declaram não haver conflitos de interesse a informar.</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Figuras | Tabelas</h4>
+</div>
+<div class="modal-body">
+<ul class="nav nav-tabs md-tabs" role="tablist">
+<li role="presentation" class="col-md-4 col-sm-4 active"><a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">Figuras
+                    (3)
+                </a></li>
+<li role="presentation" class="col-md-4 col-sm-4 "><a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">Tabelas
+                    (4)
+                </a></li>
+</ul>
+<div class="clearfix"></div>
+<div class="tab-content">
+<div role="tabpanel" class="tab-pane active" id="figures">
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFig"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf2"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf2.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 2.</strong><br>Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf3"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf3.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 3.</strong><br>Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+</div>
+<div role="tabpanel" class="tab-pane " id="tables">
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tablela 2</strong></strong><br> Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Table 3.</strong></strong><br> Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 4. </strong></strong><br> Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.</div>
+</div>
+</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFig" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf1.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 1.   Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf1.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf1.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1"><span class="sci-ico-fileFigure"></span>Figure 1</a>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf2.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 2.   Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf2.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf2.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>Figure 2</a>. Correlation between total phenol content and IC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf3.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 3.   Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf3.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf3.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>Figure 3</a>. Correlation between IC50 and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 1.</strong>    Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col>
+<col>
+<col>
+</colgroup>
+<thead><tr>
+<th align="left">Espécies</th>
+<th align="left">Nome popular</th>
+<th align="center">Local de coleta</th>
+<th align="center">No. HUVA</th>
+</tr></thead>
+<tbody>
+<tr>
+<td align="left">
+<i>S. alata</i> (L.) Roxb.</td>
+<td align="left">fedegoso-gigante</td>
+<td align="center">Sobral</td>
+<td align="center">21547</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (L.) H.S.Irwin &amp; Barneby</td>
+<td align="left">fedegoso-brando</td>
+<td align="center">Graça</td>
+<td align="center">21775</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (L.) Link</td>
+<td align="left">café-negro</td>
+<td align="center">Graça</td>
+<td align="center">21774</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Lam.) H.S.Irwin &amp; Barneby<sup>*</sup>
+</td>
+<td align="left">cássia-de-sião</td>
+<td align="center">Sobral</td>
+<td align="center">21578</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Benth.) H.S.Irwin &amp; Barneby<sup>**</sup>
+</td>
+<td align="left">pau-de-besouro</td>
+<td align="center">Graça</td>
+<td align="center">21776</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>Table 1</a>Identification of <i>Senna Senna</i> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</div></li></ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tablela 2</strong>    Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup><col span="11"></colgroup>
+<thead>
+<tr><th align="center" colspan="11">Espécies </th></tr>
+<tr>
+<th align="left">Metabólitos</th>
+<th align="left" colspan="2"><i>S. alata</i></th>
+<th align="left" colspan="2"><i>S. obtusifolia</i></th>
+<th align="left" colspan="2"><i>S. occidentalis</i></th>
+<th align="left" colspan="2"><i>S. siamea</i></th>
+<th align="left" colspan="2"><i>S. trachypus</i></th>
+</tr>
+<tr>
+<th align="left">Extratos</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">Flavonoides</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Fenóis</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Saponinas</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">+</td>
+<td align="left">-</td>
+</tr>
+<tr>
+<td align="left">Taninos</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Esteroides</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Alcaloides</td>
+<td align="left">+</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+</tr>
+<tr>
+<td align="left">Triterpenoides</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>Table 2</a>. Phytochemical screening of EEF and EEC of <i>Senna</i> Mill. (Fabaceae) species. Present: + Absent: - EEF: Ethanol extract of the leaf. EEC: Ethanol extract from the stem.</div></li></ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Table 3.</strong>    Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col span="2">
+<col span="2">
+<col span="2">
+</colgroup>
+<thead>
+<tr>
+<th align="left" rowspan="2">Espécies</th>
+<th align="center" colspan="2">Fenois<sup>1</sup> mg EAG.g<sup>-1</sup> de extrato </th>
+<th align="center" colspan="2">DPPH<sup>2</sup> CE<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+<th align="center" colspan="2"> AChEI<sup>3</sup> CI<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+</tr>
+<tr>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">
+<i>S. alata</i> (Folhas)</td>
+<td align="center">53,76 <sup>f</sup>
+</td>
+<td align="center">± 0,74</td>
+<td align="center">3,70 <sup>e</sup>
+</td>
+<td align="center">± 0,04</td>
+<td align="center">49,42 <sup>f</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. alata</i> (Caule)</td>
+<td align="center">43,44 <sup>g</sup>
+</td>
+<td align="center">± 0,21</td>
+<td align="center">5,41 <sup>c</sup>
+</td>
+<td align="center">± 0,06</td>
+<td align="center">53,25 <sup>d</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (Folhas)</td>
+<td align="center">76,32 <sup>e</sup>
+</td>
+<td align="center">± 0,41</td>
+<td align="center">4,24 <sup>d</sup>
+</td>
+<td align="center">± 0,06</td>
+<td align="center">50,37 <sup>e</sup>
+</td>
+<td align="center">± 0,32</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (Caule)</td>
+<td align="center">86,20 <sup>d</sup>
+</td>
+<td align="center">± 0,99</td>
+<td align="center">3,00 <sup>g</sup>
+</td>
+<td align="center">± 0,05</td>
+<td align="center">56,90 <sup>c</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (Folhas)</td>
+<td align="center">32,60 <sup>h</sup>
+</td>
+<td align="center">± 0,53</td>
+<td align="center">8,20 <sup>b</sup>
+</td>
+<td align="center">± 0,07</td>
+<td align="center">58,76 <sup>b</sup>
+</td>
+<td align="center">± 0,78</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (Caule)</td>
+<td align="center">30,03 <sup>h</sup>
+</td>
+<td align="center">± 1,00</td>
+<td align="center">11,19 <sup>a</sup>
+</td>
+<td align="center">± 0,15</td>
+<td align="center">57,26 <sup>c</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Folhas)</td>
+<td align="center">51,73 <sup>f</sup>
+</td>
+<td align="center">± 0,85</td>
+<td align="center">3,34 <sup>f</sup>
+</td>
+<td align="center">± 0,05</td>
+<td align="center">59,77 <sup>a</sup>
+</td>
+<td align="center">± 0,26</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Caule)</td>
+<td align="center">111,7 <sup>c</sup>
+</td>
+<td align="center">± 3,43</td>
+<td align="center">0,83 <sup>i</sup>
+</td>
+<td align="center">± 0,01</td>
+<td align="center">59,52 <sup>ab</sup>
+</td>
+<td align="center">± 0,15</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Folhas)</td>
+<td align="center">184,80 <sup>b</sup>
+</td>
+<td align="center">± 5,09</td>
+<td align="center">0,63 <sup>k</sup>
+</td>
+<td align="center">± 0,01</td>
+<td align="center">32,40 <sup>g</sup>
+</td>
+<td align="center">± 0,12</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Caule)</td>
+<td align="center">191,3 <sup>a</sup>
+</td>
+<td align="center">± 0,47</td>
+<td align="center">2,52 <sup>h</sup>
+</td>
+<td align="center">± 0,03</td>
+<td align="center">31,44 <sup>h</sup>
+</td>
+<td align="center">± 0,14</td>
+</tr>
+<tr>
+<td align="left">Quercetina</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">1,03 <sup>i</sup>
+</td>
+<td align="center">± 0,00</td>
+<td align="center">-</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">Fisiostigmina</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">1,15 <sup>i</sup>
+</td>
+<td align="center">± 0,00</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote">
+<li><div>Total phenol content, antioxidant activity and acetylcholinesterase enzyme inhibition of <i>Senna</i> Mill. (Fabaceae) species. </div></li>
+<li><div>Todas as análises foram realizadas em triplicada e os resultados foram expressos como média ± desvio padrão. As diferenças entre os valores foram examinadas usando análise de variância (ANOVA) e os resultados foram comparados usando o teste de Tukey com 95% nível de confiança. Letras diferentes denotam diferença estatística entre os valores de cada coluna (p &lt; 0,05). <sup>1</sup>Miligrama equivalente ao Ácido Gálico por grama de extrato; <sup>2</sup>Concentração efetiva para inibir 50% do radical livre DPPH (2,2 -difenil-1-picril-hidrazil); <sup>3</sup>Concentração inibitória capaz de inibir 50% da acetilcolinesterase. (-) Testes não realizados.</div></li>
+<li><div>All analyzes were performed in triplicate and the results were expressed as mean ± standard deviation. The differences between the values ​​were examined using analysis of variance (ANOVA) and the results were compared using the Tukey test at 95% confidence level. Different letters denote statistical difference between the values ​​of each column (p &lt;0.05). <sup>1</sup> milligram Equivalent to Gallic Acid per gram of extract; <sup>2</sup>Effective concentration to inhibit 50% of the free radical DPPH (2,2 - diphenyl - 1 - picryl - hydrazil); <sup>3</sup>Inhibitory concentration capable of inhibiting 50% of acetylcholinesterase. (-) Tests not performed.</div></li>
+</ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 4. </strong>    Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col>
+<col span="2">
+<col span="2">
+<col span="2">
+<col span="2">
+</colgroup>
+<thead>
+<tr>
+<th align="left" rowspan="4">Espécies</th>
+<th align="center" rowspan="4">Extrato</th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+</tr>
+<tr>
+<th align="center" colspan="2">LABIMIC 5906 </th>
+<th align="center" colspan="2">LABIMIC 6213 </th>
+<th align="center" colspan="2">LABIMIC 6205 </th>
+<th align="center" colspan="2">LABIMIC 6753 </th>
+</tr>
+<tr>
+<th align="center">CIM</th>
+<th align="center">CFM </th>
+<th align="center">CIM </th>
+<th align="center">CFM</th>
+<th align="center">CIM</th>
+<th align="center">CFM</th>
+<th align="center">CIM</th>
+<th align="center">CFM</th>
+</tr>
+<tr>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left" rowspan="2"><i>S. alata</i></td>
+<td align="center">EEF</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. obtusifolia</i></td>
+<td align="center">EEF</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. occidentalis</i></td>
+<td align="center">EEF</td>
+<td align="center">0,07</td>
+<td align="center">0,15</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. siamea</i></td>
+<td align="center">EEF</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. trachypus</i></td>
+<td align="center">EEF</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="left">Cetoconazol</td>
+<td align="center"> </td>
+<td align="center">2,0</td>
+<td align="center"> </td>
+<td align="center">1,0</td>
+<td align="center"> </td>
+<td align="center">1,0</td>
+<td align="center"> </td>
+<td align="center">0,5</td>
+<td align="center"> </td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>Table 4</a>.  Minimum Inhibitory Concentration (MIC) and Minimum Fungicidal Concentration (MFC) of ethanolic extracts (EEs) from <i>Senna</i> Mill. LABIMIC: Microbiology Laboratory; EEF: Ethanol extract of the leaf; EEC: Ethanol extract from the stem; NI: It didn't inhibit. (Fabaceae) species compared to <i>Trichophyton rubrum</i> species.</div></li></ul></div></div>
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+            function currentDate() {
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+            var months = ['Janeiro', 'Fevereiro', 'Março', 'Abril', 'Maio', 'Junho', 'Julho', 'Agosto', 'Setembro', 'Outubro', 'Novembro', 'Dezembro']
+            today.setTime(today.getTime());
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+            var citation = 'Neves, Andréa Maria et al. Prospecção química, atividade antioxidante, anticolinesterásica e antifúngica de extratos etanólicos de espécies de Senna Mill. (Fabaceae). Hoehnea [online]. 2022, v. 49 [Acessado CURRENTDATE] , e1112020. Disponível em: &lt;https://doi.org/10.1590/2236-8906-111/2020&gt;. Epub 21 Fev 2022. ISSN 2236-8906. https://doi.org/10.1590/2236-8906-111/2020.'.replace('CURRENTDATE', currentDate());
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diff --git a/tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020.xml b/tests/fixtures/fig_sem_id/2236-8906-hoehnea-49-e1112020/2236-8906-hoehnea-49-e1112020.xml
new file mode 100644
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@@ -0,0 +1,2597 @@
+<?xml version="1.0" encoding="utf-8"?>
+<!DOCTYPE article
+  PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Publishing DTD v1.1 20151215//EN" "https://jats.nlm.nih.gov/publishing/1.1/JATS-journalpublishing1.dtd">
+<article article-type="research-article" dtd-version="1.1" specific-use="sps-1.9" xml:lang="pt" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink">
+	<front>
+		<journal-meta>
+			<journal-id journal-id-type="publisher-id">hoehnea</journal-id>
+			<journal-title-group>
+				<journal-title>Hoehnea</journal-title>
+				<abbrev-journal-title abbrev-type="publisher">Hoehnea</abbrev-journal-title>
+			</journal-title-group>
+			<issn pub-type="ppub">0073-2877</issn>
+			<issn pub-type="epub">2236-8906</issn>
+			<publisher>
+				<publisher-name>Instituto de Pesquisas Ambientais</publisher-name>
+			</publisher>
+		</journal-meta>
+		<article-meta>
+			<article-id pub-id-type="doi">10.1590/2236-8906-111/2020</article-id>
+            <article-id pub-id-type="other">00208</article-id>
+			<article-categories>
+				<subj-group subj-group-type="heading">
+					<subject>Artigo</subject>
+				</subj-group>
+			</article-categories>
+			<title-group>
+				<article-title>Prospecção química, atividade antioxidante, anticolinesterásica e antifúngica de extratos etanólicos de espécies de <italic>Senna</italic> Mill. (Fabaceae)</article-title>
+				<trans-title-group xml:lang="en">
+					<trans-title>Chemical prospecting and antioxidant, anticholinesterase and antifungal activity of ethanol extracts from <italic>Senna</italic> Mill. species. (Fabaceae)</trans-title>
+				</trans-title-group>
+			</title-group>
+			<contrib-group>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-7388-1844</contrib-id>
+					<name>
+						<surname>Neves</surname>
+						<given-names>Andréa Maria</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
+					<xref ref-type="corresp" rid="c1"><sup>4</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-2766-3790</contrib-id>
+					<name>
+						<surname>Morais</surname>
+						<given-names>Selene Maia de</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0001-5527-164X</contrib-id>
+					<name>
+						<surname>Santos</surname>
+						<given-names>Hélcio Silva dos</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0003-2503-9772</contrib-id>
+					<name>
+						<surname>Ferreira</surname>
+						<given-names>Marcílio Matos</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-2035-0425</contrib-id>
+					<name>
+						<surname>Cruz</surname>
+						<given-names>Ricardo Carneiro Vera</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-5222-4378</contrib-id>
+					<name>
+						<surname>Souza</surname>
+						<given-names>Elnatan Bezerra de</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-4384-5738</contrib-id>
+					<name>
+						<surname>Andrade</surname>
+						<given-names>Lúcia Betânia da Silva</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
+				</contrib>
+				<contrib contrib-type="author">
+					<contrib-id contrib-id-type="orcid">0000-0002-8865-5954</contrib-id>
+					<name>
+						<surname>Fontenelle</surname>
+						<given-names>Raquel Oliveira dos Santos</given-names>
+					</name>
+					<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
+				</contrib>
+			</contrib-group>
+			<aff id="aff1">
+				<label>1</label>
+				<institution content-type="original"> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil</institution>
+				<institution content-type="orgname">Universidade Estadual do Ceará</institution>
+				<institution content-type="orgdiv1">Centro de Ciências e Tecnologia</institution>
+				<institution content-type="orgdiv2">Programa de Pós-graduação em Biotecnologia</institution>
+				<addr-line>
+					<postal-code>60740-000</postal-code>
+					<city>Fortaleza</city>
+					<state>CE</state>
+				</addr-line>
+				<country country="BR">Brasil</country>
+			</aff>
+			<aff id="aff2">
+				<label>2</label>
+				<institution content-type="original"> Universidade Estadual Vale do Acaraú, Centro de Ciências Exatas e Tecnologia, Curso de Química, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</institution>
+				<institution content-type="orgname">Universidade Estadual Vale do Acaraú</institution>
+				<institution content-type="orgdiv1">Centro de Ciências Exatas e Tecnologia</institution>
+				<institution content-type="orgdiv2">Curso de Química</institution>
+				<addr-line>
+					<postal-code>62040-370</postal-code>
+					<city>Sobral</city>
+					<state>CE</state>
+				</addr-line>
+				<country country="BR">Brasil</country>
+			</aff>
+			<aff id="aff3">
+				<label>3</label>
+				<institution content-type="original"> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</institution>
+				<institution content-type="orgname">Universidade Estadual Vale do Acaraú</institution>
+				<institution content-type="orgdiv1">Centro de Ciências Agrárias e Biológicas</institution>
+				<institution content-type="orgdiv2">Curso de Ciências Biológicas</institution>
+				<addr-line>
+					<postal-code>62040-370</postal-code>
+					<city>Sobral</city>
+					<state>CE</state>
+				</addr-line>
+				<country country="BR">Brasil</country>
+			</aff>
+			<author-notes>
+				<corresp id="c1">
+					<label><sup>4</sup></label> Autor para correspondência: <email>andreamarianeves@gmail.com</email>
+				</corresp>
+				<fn fn-type="edited-by" id="fn1">
+					<label>Editora Associada:</label>
+					<p> Catarina Carvalho Nievola</p>
+				</fn>
+				<fn fn-type="con" id="fn2">
+					<label>Contribuição dos autores</label>
+					<p><bold>Andréa Maria Neves:</bold> Contribuição substancial em todas as etapas da pesquisa e para a confecção do manuscrito. <bold>Selene Maia de Morais:</bold> Contribuição na realização do teste de acetilcolinesterase; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <bold>Hélcio Silva dos Santos:</bold> Contribuição na preparação dos extratos; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <bold>Marcílio Matos Ferreira:</bold> Contribuição para a coleta das espécies e preparação dos extratos. <bold>Ricardo Carneiro Vera Cruz:</bold> Contribuição na realização dos testes fitoquímicos e quantificação de fenóis totais. <bold>Elnatan Bezerra de Souza:</bold> Contribuição na coleta e identificação das espécies; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <bold>Lúcia Betânia da Silva Andrade:</bold> Contribuição na realização da atividade antioxidante, para a interpretação dos dados, e para revisão crítica, agregando conteúdo intelectual. <bold>Raquel Oliveira dos Santos Fontenelle:</bold> Contribuição nos testes antifúngicos e para revisão crítica, agregando conteúdo intelectual. </p>
+				</fn>
+				<fn fn-type="conflict" id="fn3">
+					<label>Conflitos de interesse</label>
+					<p> Os autores declaram não haver conflitos de interesse a informar.</p>
+				</fn>
+			</author-notes>
+			<pub-date date-type="pub" publication-format="electronic">
+				<day>21</day>
+				<month>02</month>
+				<year>2022</year>
+			</pub-date>
+			<pub-date date-type="collection" publication-format="electronic">
+				<year>2022</year>
+			</pub-date>
+			<volume>49</volume>
+			<elocation-id>e1112020</elocation-id>
+			<history>
+				<date date-type="received">
+					<day>14</day>
+					<month>10</month>
+					<year>2020</year>
+				</date>
+				<date date-type="accepted">
+					<day>03</day>
+					<month>12</month>
+					<year>2021</year>
+				</date>
+			</history>
+			<permissions>
+				<license license-type="open-access" xlink:href="https://creativecommons.org/licenses/by/4.0/" xml:lang="pt">
+					<license-p>Este é um artigo publicado em acesso aberto sob uma licença Creative Commons</license-p>
+				</license>
+			</permissions>
+			<abstract>
+				<title>RESUMO</title>
+				<p>O objetivo deste trabalho foi avaliar o perfil químico, teor de fenóis totais e as atividades antioxidante, antiacetilcolinesterásica e antifúngica dos extratos etanólicos das folhas (EEF) e do caule (EEC) de cinco espécies de <italic>Senna</italic>, bem como avaliar a correlação entre o conteúdo de fenóis totais com a atividade sequestradora do radical livre DPPH e com a inibição da enzima acetilcolinesterase AChEI. No teste fitoquímico, evidenciou-se a presença de metabólitos secundários em todos os extratos. Os EEF e EEC de <italic>Senna trachypus</italic>, destacaram-se por apresentar os maiores valores de fenóis totais. Os EEF e EEC de <italic>S. trachypus</italic> mostraram a melhor ação sobre a enzima acetilcolinesterase. Todas as espécies apresentaram atividade antioxidante, em especial o EEF de <italic>S. trachypus</italic>. Foi observado correlação forte para as variáveis fenóis totais e atividade antioxidante (r = -0,71), muito forte para fenóis totais e antiacetilcolinesterase (r = -0,84) e atividade moderada para atividade antioxidante e antiacetilcolinesterase (0,43). Apenas os extratos de <italic>S. trachypus</italic> apresentaram atividade contra todos os dermatófitos, quando comparado às demais espécies. A espécie <italic>S. trachypus</italic> foi considerada a planta mais promissora para estudos subsequentes, a fim de encontrar compostos com ações farmacológicas. </p>
+			</abstract>
+			<trans-abstract xml:lang="en">
+				<title>ABSTRACT</title>
+				<p>The objective of this work was to evaluate the chemical profile, total phenol content and the antioxidant, antiacetylcholinesterase and antifungal activities of ethanol extracts from leaves (EEF) and stem (EEC) of five species of <italic>Senna</italic>, as well as to evaluate the correlation between the content of total phenols with the DPPH free radical scavenging activity and with the inhibition of the acetylcholinesterase AChEI enzyme. The phytochemical test showed the presence of secondary metabolites in all extracts. The EEF and EEC of <italic>Senna trachypus</italic>, stood out for presenting the highest values of total phenols. <italic>S. trachypus</italic> EEF and EEC showed the best action on the acetylcholinesterase enzyme. All species showed antioxidant activity, especially the EEF from <italic>S. trachypus</italic>. A strong correlation was observed for the variables total phenols and antioxidant activity (r = -0.71), very strong for total phenols and anti-acetylcholinesterase (r = -0.84) and moderate activity for antioxidant and anti-acetylcholinesterase activity (r = 0.43). Only <italic>S. trachypus</italic> extracts showed activity against all dermatophytes, when compared to the other species. The species <italic>S. trachypus</italic> was considered the most promising plant for further studies, in order to find compounds with pharmacological actions.</p>
+			</trans-abstract>
+			<kwd-group xml:lang="pt">
+				<title>Palavras-chave:</title>
+				<kwd>acetilcolinesterase</kwd>
+				<kwd>dermatófitos</kwd>
+				<kwd>fitoquímica</kwd>
+				<kwd>produtos naturais</kwd>
+				<kwd>radicais livres</kwd>
+			</kwd-group>
+			<kwd-group xml:lang="en">
+				<title>Keywords:</title>
+				<kwd>acetylcholinesterase</kwd>
+				<kwd>dermatophytes</kwd>
+				<kwd>phytochemistry</kwd>
+				<kwd>natural products</kwd>
+				<kwd>free radicals</kwd>
+			</kwd-group>
+			<funding-group>
+				<award-group award-type="contract">
+					<funding-source>FUNCAP</funding-source>
+					<award-id>PBI3-0139-00252.01.00/18</award-id>
+					<award-id>BP4-0172-00170.01.00/20</award-id>
+				</award-group>
+			</funding-group>
+			<counts>
+				<fig-count count="3"/>
+				<table-count count="4"/>
+				<equation-count count="0"/>
+				<ref-count count="56"/>
+			</counts>
+		</article-meta>
+	</front>
+	<body>
+		<sec sec-type="intro">
+			<title>Introdução</title>
+			<p><italic>Senna</italic> Mill. é um gênero monofilético com distribuição pantropical e ampla variedade morfológica (<xref ref-type="bibr" rid="B41">Pellerin <italic>et al</italic>. 2019</xref>). Possuindo aproximadamente 300 espécies, das quais 200 nas Américas, este gênero é o segundo maior da família Fabaceae (<xref ref-type="bibr" rid="B43">Queiroz 2009</xref>, <xref ref-type="bibr" rid="B22">Kim <italic>et al</italic>. 2018</xref>, <xref ref-type="bibr" rid="B53">Souza &amp; Silva 2016</xref>). O gênero é representado no Brasil por 79 espécies, onde 29 são endêmicas, sendo a região Nordeste a que apresenta a maior riqueza de espécies com 53 registros (<xref ref-type="bibr" rid="B7">BFG 2018</xref>). </p>
+			<p>Trata-se de um gênero muito expressivo na flora do semiárido, alcançando destaque no Domínio Fitogeográfico da Caatinga, onde são catalogadas 42 espécies (<xref ref-type="bibr" rid="B50">Souza &amp; Bortoluzzi 2015</xref>). As espécies de <italic>Senna</italic> são geralmente arbustos ou arvoretas, raramente ervas ou subarbustos anuais. Entre as suas características diagnósticas estão os nectários extraflorais convexos, interfoliolares, flores vistosas, com pétalas amarelo-brilhantes, anteras amarelas, rígidas, com deiscência abrindo por poros ou fendas, ausência de bractéolas no pedicelo, frutos deiscentes plano-compressos ou indeiscentes e cilíndricos (<xref ref-type="bibr" rid="B43">Queiroz 2009</xref>).</p>
+			<p>As espécies de <italic>Senna</italic> têm diversas aplicações medicinais e são eficazes no tratamento para uma série de doenças, como malária, micose, dengue, eczema, hepatite e dermatite, sendo também indicadas como anti-hipertensivo, vermífugo, laxante, abortivo e antitussígeno (<xref ref-type="bibr" rid="B28">Macedo <italic>et al.</italic> 2016</xref>, <xref ref-type="bibr" rid="B8">Bieski <italic>et al</italic>. 2015</xref>, <xref ref-type="bibr" rid="B21">Kabir <italic>et al.</italic> 2014</xref>). Além de suas aplicações farmacológicas, estudos têm revelado que espécies pertencentes a este gênero possuem, em sua composição, uma vasta diversidade de princípios bioativos que estão associadas a diferentes atividades biológicas. Neste sentido, podemos citar como exemplo as atividades antioxidantes, antitumoral, antibacterianas, antifúngicas e anti-inflamatórias (<xref ref-type="bibr" rid="B34">Neves <italic>et al.</italic> 2017</xref>).</p>
+			<p>As plantas são fontes alternativas promissoras de substâncias de interesse biológico e farmacológico, já que podem produzir, a partir de seu metabolismo secundário, uma enorme diversidade de substâncias, dentre estas, os compostos fenólicos. Alguns estudos têm revelado que os compostos fenólicos são responsáveis por várias atividades biológicas, incluindo atividade antifúngica. Esta atividade pode ser direta nos micro-organismos, ou sobre outros fatores necessários para a expressão da virulência ou patogenicidade (<xref ref-type="bibr" rid="B45">Rodrigues <italic>et al</italic>. 2019</xref>).</p>
+			<p>Os compostos fenólicos estão entre os metabólitos secundários mais estudados, notadamente por possuírem grande potencial para atividades antioxidantes, atuando na redução do risco de algumas doenças agudas e crônicas relacionadas ao estado redox do corpo humano, ocasionadas pelos radicais livres. Estas moléculas apresentam uma alta capacidade reativa, sendo consideradas perigosas para os organismos vivos, causando doenças prejudiciais, incluindo doenças neurodegenerativas, como o mal de Alzheimer (DA). Atualmente, uma das teorias mais aceitas na abordagem padrão no tratamento sintomático dessa demência é a “hipótese colinérgica”. Portanto, os inibidores da enzima acetilcolinesterase (AChEI) preservam os níveis de acetilcolina, melhorando a eficiência da transmissão colinérgica (<xref ref-type="bibr" rid="B4">Bardakci <italic>et al</italic>. 2019</xref>, <xref ref-type="bibr" rid="B27">Lim <italic>et al</italic>. 2019</xref>; <xref ref-type="bibr" rid="B35">Neagu <italic>et al</italic>. 2016</xref>).</p>
+			<p>Por este motivo, a utilização de dietas ricas ou enriquecidas com antioxidantes podem prevenir, ou pelo menos amenizar, a deterioração orgânica por um excessivo estresse oxidativo. Além disso, o crescimento sobre a investigação científica envolvendo os efeitos antioxidantes de extratos brutos, frações purificadas, ou mesmo de compostos isolados, onde estão classificados os compostos fenólicos, são demonstrados em muitos estudos (<xref ref-type="bibr" rid="B42">Penido <italic>et al.</italic> 2017</xref>, <xref ref-type="bibr" rid="B30">Morais <italic>et al.</italic> 2013</xref>).</p>
+			<p>Desta forma, investigar a atividade antifúngica e anticolinesterásica de extratos de espécies de <italic>Senna</italic>, analisando o seu potencial antioxidante, o seu teor de fenóis totais e o seu perfil fitoquímico, são maneiras de promover tanto o conhecimento acerca dessas espécies, como também potencializar o descobrimento de novos fitofármacos para o combate de inúmeras enfermidades. Assim, este trabalho avaliou o perfil fitoquímico, o teor de fenóis totais e as atividades antioxidante, anticolinesterásica e antifúngica dos extratos etanólicos de <italic>S. alata</italic> (L.) Roxb., <italic>S. obtusifolia</italic> (L.) H.S.Irwin &amp; Barneby, <italic>S. occidentalis</italic> (L.) Link, <italic>S. siamea</italic> (Lam.) H.S.Irwin &amp; Barneby e <italic>S. trachypus</italic> (Benth.) H.S.Irwin &amp; Barneby, e a correlação entre o teor de fenóis totais e as atividades antioxidante e anticolinesterásica. </p>
+		</sec>
+		<sec sec-type="materials|methods">
+			<title>Materiais e métodos</title>
+			<p>Material vegetal e preparação dos extratos - Foram selecionadas para este estudo cinco espécies de <italic>Senna</italic>, sendo uma exótica naturalizada e quatro nativas, das quais uma é endêmica do Brasil, ocorrendo no Cerrado e na Caatinga (<xref ref-type="bibr" rid="B7">BFG 2018</xref>) (<xref ref-type="table" rid="t1">Tabela 1</xref>). As folhas e caules de <italic>Senna</italic> spp. foram coletados em diferentes locais da região Noroeste do Ceará. A identificação botânica das espécies foi realizada no Herbário Francisco José de Abreu Matos da Universidade Estadual Vale do Acaraú (HUVA), pelo professor Dr. Elnatan Bezerra de Souza. Para o preparo dos extratos, 200g das folhas e caule secos de cada espécie de um mesmo indivíduo foram triturados e imersos durante 10 dias em 500 mL de etanol e, na sequência o extrato foi filtrado e concentrado em um evaporador rotativo a (60°C) durante 2 h. Após este processo, foi mantido em banho-maria (40°C) até a eliminação total do solvente, obtendo-se o extrato etanólico das folhas (EEF) e extrato etanólico do caule (EEC) (<xref ref-type="bibr" rid="B29">Matos 2009</xref>).</p>
+			<p>
+				<table-wrap id="t1">
+					<label>Tabela 1.</label>
+					<caption>
+						<title>Identificação das espécies de <italic>Senna</italic> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</title>
+					</caption>
+					<table>
+						<colgroup>
+							<col/>
+							<col/>
+							<col/>
+							<col/>
+						</colgroup>
+						<thead>
+							<tr>
+								<th align="left">Espécies</th>
+								<th align="left">Nome popular</th>
+								<th align="center">Local de coleta</th>
+								<th align="center">No. HUVA</th>
+							</tr>
+                        </thead>
+                        <tbody>
+							<tr>
+								<td align="left"><italic>S. alata</italic> (L.) Roxb.</td>
+								<td align="left">fedegoso-gigante</td>
+								<td align="center">Sobral</td>
+								<td align="center">21547</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. obtusifolia</italic> (L.) H.S.Irwin &amp; Barneby</td>
+								<td align="left">fedegoso-brando</td>
+								<td align="center">Graça</td>
+								<td align="center">21775</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. occidentalis</italic> (L.) Link</td>
+								<td align="left">café-negro</td>
+								<td align="center">Graça</td>
+								<td align="center">21774</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. siamea</italic> (Lam.) H.S.Irwin &amp; Barneby<sup>*</sup></td>
+								<td align="left">cássia-de-sião</td>
+								<td align="center">Sobral</td>
+								<td align="center">21578</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. trachypus</italic> (Benth.) H.S.Irwin &amp; Barneby<sup>**</sup></td>
+								<td align="left">pau-de-besouro</td>
+								<td align="center">Graça</td>
+								<td align="center">21776</td>
+							</tr>
+						</tbody>
+					</table>
+                    <table-wrap-foot>
+                        <fn id="TFN1">
+                            <p><xref ref-type="table" rid="t1">Table 1</xref>Identification of <italic>Senna Senna</italic> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</p>
+                        </fn>
+                    </table-wrap-foot>
+				</table-wrap>
+			</p>
+			<p>Triagem fitoquímica - Os extratos etanólicos foram submetidos a triagem fitoquímica, tomando como referência a metodologia descrita por <xref ref-type="bibr" rid="B29">Matos (2009</xref>). Através deste ensaio preliminar, foi possível verificar as principais classes de metabólitos secundários por meio de reações químicas que resultaram no aparecimento de coloração e/ou precipitado, característico para cada classe de substância. Os ensaios foram conduzidos para as seguintes classes de substâncias: fenóis, taninos, flavonoides, saponinas, esteroides, triterpenoides e alcaloides. Todos os testes foram realizados em triplicata procedimentais. </p>
+			<p>Determinação do teor de fenóis totais - O teor de fenóis totais nos extratos etanólicos foi determinado pelo método espectrofotométrico de Folin-Ciocateau, utilizando ácido gálico como padrão de referência (<xref ref-type="bibr" rid="B23">Kim <italic>et al.</italic> 2006</xref>). Em cada tubo adicionou-se 0,2 mL de cada extrato nas concentrações (0,62; 0,31 e 0,15 mg mL<sup>-1</sup>) com 1 mL do reagente Folin-Ciocalteau agitado por 2 minutos e adicionado 0,8 mL de carbonato de sódio (Na<sub>2</sub>CO<sub>3</sub>) 7,5% (m/v). Para o tubo controle foi utilizado 1 mL do reagente Folin- Ciocalteau com 0,8 mL de Na<sub>2</sub>CO<sub>3</sub> e 0,2 mL de etanol, em triplicata. Os tubos foram deixados em banho-maria a 37 ̊C por 30 minutos na ausência de luz. Logo em seguida, foi realizado a leitura dos tubos em comprimento de onda de 765 nm. O teor de fenóis foi calculado e expresso em mg de equivalente de ácido gálico por grama de extrato (EAG.g<sup>-1</sup>), com base numa curva padrão preparada com ácido gálico. Todos os testes foram realizados em triplicata.</p>
+			<p>Atividade antioxidante - A atividade antioxidante dos extratos foi determinada pelo método de redução do radical 2,2’-difenil-1-picril-hidrazil (DPPH), segundo a metodologia modificada por <xref ref-type="bibr" rid="B9">Brand-Williams <italic>et al.</italic> (1995</xref>), <xref ref-type="bibr" rid="B48">Sanchez-Moreno <italic>et al</italic>. (1998</xref>). Foram preparadas soluções etanólicas das amostras nas concentrações de 5,0; 2,5; 1,25; 0,62; 0,31 e 0,15 mg mL<sup>-1</sup>. Foram utilizados 100 µL dos extratos com 2,4 mL de DPPH (0,04 mg mL<sup>-1</sup>). Para o tubo controle foram utilizados 100 µL de etanol com 2,4 mL de DPPH em triplicata. O meio reacional ficou por 30 minutos na ausência da luz, e posteriormente foi realizada a leitura em comprimento de onda 515 nm. A atividade sequestradora do radical DPPH pelos extratos nas diferentes concentrações foi calculada pela expressão do índice de varredura em porcentagem (IV%): IV% = (Abs <sub>DPPH</sub> - Abs <sub>Amostra</sub> / Abs <sub>DPPH</sub>) x 100. A concentração efetiva para inibir 50% do radical livre DPPH (CE<sub>50</sub>) foi obtida com auxílio do Software Excel 2019, onde, a partir dos valores das concentrações finais da amostra e o índice de varredura (IV%), foram originados gráficos de dispersão cujas equações das retas foram utilizadas para se obter os valores da média e desvio padrão. Para fins de comparação, foi construída uma curva de calibração com diferentes porcentagens do flavonoide quercetina, que apresenta elevada atividade antioxidante em radical livre DPPH.</p>
+			<p>Avaliação da atividade anticolinesterásica <italic>in vitro</italic> - O ensaio para verificação da inibição da enzima acetilcolinesterase (AChE) dos extratos foi realizado de acordo com a metodologia descrita por <xref ref-type="bibr" rid="B14">Ellman <italic>et al.</italic> (1961</xref>). Em placas estéreis de 96 poços, foram adicionados 25 µL de iodeto de acetiltiocolina (15 mM), 125 µL de 5,5’-ditiobis-[2-nitrobenzóico] na solução Tris/HCL (50 nM, pH 8, com 0,1 M de NaCL e 0,02 M de MgCL<sub>2</sub> .6H<sub>2</sub>O. (3 mM, DTNB ou reagente de Ellman)), 50 µL da solução Tris/HCL (50 nM, pH 8, com 0,1% de albumina sérica bovina (BSA) e 25 µL dos extratos de <italic>Senna</italic> spp. na concentraçao de 0,2 mg.mL<sup>-1</sup> em tampão Tris/HCL (50 mM, pH 8) de 0,2 mg.mL<sup>-1</sup> (<xref ref-type="bibr" rid="B44">Rhee <italic>et al.</italic> 2001</xref>, <xref ref-type="bibr" rid="B54">Trevisan <italic>et al.</italic> 2003</xref>). </p>
+			<p>A absorbância foi aferida a 405 nm durante 30 segundos. Em seguida, foram adicionados 25 µL da enzima acetilcolinesterase (0,25 U.mL<sup>-1</sup>) e a absorbância foi aferida por minuto até o total de 25 minutos de incubação da enzima. Como padrão negativo foram utilizadas todas as soluções, excetuando-se a amostra. O padrão utilizado como controle positivo foi a fisostigmina (0,22 mg.mL<sup>-1</sup>.) e todas as amostras foram analisadas em triplicata. A atividade anticolinesterásica dos extratos vegetais foi determinada de acordo com os valores de CI<sub>50</sub> (Concentração inibitória capaz de inibir 50% da enzima acetilcolinesterase) como: alta potência (CI<sub>50</sub> &lt; 20 μg. mL<sup>-1</sup>); potência moderada (20 &lt; CI<sub>50</sub> &lt; 200 μg.mL<sup>-1</sup>) e baixa potência (200 &lt; CI<sub>50</sub> &lt; 1000 μg.mL<sup>-1</sup>) (<xref ref-type="bibr" rid="B46">Santos <italic>et al</italic>. 2018</xref>).</p>
+			<p>Ensaio antifúngico <italic>in vitro</italic> - No ensaio para verificação da concentração inibitória mínima (CIM) dos EE das espécies de <italic>Senna</italic>, foram utilizadas cepas de <italic>Trichophyton rubrum</italic> obtidas a partir da micoteca da Universidade Federal de Pernambuco e do Centro Especializado de Micologia Médica (CEMM) da Universidade Federal do Ceará<italic>.</italic> Para este ensaio foi utilizado o método de microdiluição em caldo<italic>,</italic> de acordo com a metodologia descrita por (<xref ref-type="bibr" rid="B33">Neves <italic>et al.</italic> 2019</xref>) com as normas do protocolo <xref ref-type="bibr" rid="B12">Clinical Laboratory Standards Insitute do documento M38-A (CLSI M38-A2, 2008</xref>)<italic>.</italic> Em placas de 96 poços estéreis, foram adicionados 100 µL de meio RPMI em todos os poços e 10 mg mL<sup>-1</sup> dos extratos de <italic>Senna</italic> spp. foi acrescentado a todos os poços da primeira coluna e, em sequência foram efetuadas as diluições seriadas. Finalmente, 100 µL do inóculo foi adicionado aos poços da placa. Como controle foi utilizado o Cetoconazol (Sigma, Chemical Co., USA). Para as análises de susceptibilidade, os extratos etanólicos foram testados em concentrações variando de 0,002 a 2,5 mg mL<sup>-1</sup>. As placas foram cobertas com parafilme e incubadas a 37 °C e a leitura visual foi realizada após cinco dias para <italic>T. rubrum</italic>. Procedimento realizado em duplicata. A CIM é definida como a menor concentração do extrato capaz de inibir 100% do crescimento fúngico visível (<xref ref-type="bibr" rid="B16">Fontenelle <italic>et al.</italic> 2007</xref>). A concentração fungicida mínima (CFM) foi determinada por subcultura de 100 μL da solução de poços sem turbidez no meio Ágar Dextrose de Batata, a 28 °C. (<xref ref-type="bibr" rid="B15">Fontenelle <italic>et al.</italic> 2008</xref>).</p>
+			<p>Análise estatística - Todas as determinações foram realizadas em triplicata e todos os resultados foram apresentados como média ± desvio-padrão (DP). Foram realizadas análises de variância (ANOVA) com duas repetições e o Teste Tukey, ao nível de significância de 5%, usando programa Graph Pad Prism<sup>®</sup> v5.01 (GraphPadSoftware, San Diego, CA, E.U.A.). As diferenças entre as médias foram consideradas significativas quando o valor obtido para &quot;<italic>p</italic>&quot; foi menor que 0,05 (<italic>p</italic> &lt; 0,05). </p>
+			<p>Para análises da correlação entre os dados, foi utilizado o coeficiente de correlação de Pearson no software Microsoft Excel 2019, a qual mede o grau da correlação linear entre duas variáveis quantitativas. A intensidade dessa correlação é dada pelo “r”, que é um índice adimensional com valores situados entre -1,0 e 1,0. Quando o valor de r estiver entre 0,00-0,19 a correlação é muito fraca; entre 0,20-0,39 é fraca; 0,40-0,59 é uma correlação moderada; entre 0,60-0,79 é forte e finalmente entre 0,80-1,0 diz-se que é uma correlação muito forte (<xref ref-type="bibr" rid="B32">Mukaka 2012</xref>).</p>
+		</sec>
+		<sec sec-type="results|discussion">
+			<title>Resultados e discussão<xref ref-type="table" rid="t3">Tabela 3</xref></title>
+			<p>Os fito-constituintes ou fitoquímicos são compostos químicos que desempenham importantes funções nas plantas. A triagem fitoquímica em materiais vegetais é geralmente o ponto de partida para o isolamento e purificação de compostos naturais com bioatividade (<xref ref-type="bibr" rid="B39">Omoregie &amp; Oikeh 2015</xref>). A triagem fitoquímica preliminar revelou a presença de fenóis, taninos, flavonoides e esteroides para todos os extratos estudados (<xref ref-type="table" rid="t2">Tabela 2</xref>). Entretanto, a presença de saponinas foi constatada apenas no EEF e EEC de <italic>S. alata</italic> e no EEF de <italic>S. trachypus</italic>. Já os alcaloides foram encontrados exclusivamente no EEF de <italic>S. alata</italic> e nenhuma das espécies apresentou triterpenoides. </p>
+			<p>
+				<table-wrap id="t2">
+					<label>Tablela 2</label>
+					<caption>
+						<title>Triagem fitoquímica do EEF e do EEC de espécies de <italic>Senna</italic> Mill. (Fabaceae)<italic>.</italic> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.</title>
+					</caption>
+					<table>
+						<colgroup>
+							<col span="11"/>
+						</colgroup>
+						<thead>
+							<tr>
+								<th align="center" colspan="11">Espécies </th>
+							</tr>
+							<tr>
+								<th align="left">Metabólitos</th>
+								<th align="left" colspan="2"><italic>S. alata</italic></th>
+								<th align="left" colspan="2"><italic>S. obtusifolia</italic></th>
+								<th align="left" colspan="2"><italic>S. occidentalis</italic></th>
+								<th align="left" colspan="2"><italic>S. siamea</italic></th>
+								<th align="left" colspan="2"><italic>S. trachypus</italic></th>
+							</tr>
+							<tr>
+								<th align="left">Extratos</th>
+								<th align="left">EEF</th>
+								<th align="left">EEC</th>
+								<th align="left">EEF</th>
+								<th align="left">EEC</th>
+								<th align="left">EEF</th>
+								<th align="left">EEC</th>
+								<th align="left">EEF</th>
+								<th align="left">EEC</th>
+								<th align="left">EEF</th>
+								<th align="left">EEC</th>
+							</tr>
+                        </thead>
+                        <tbody>
+							<tr>
+								<td align="left">Flavonoides</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+							</tr>
+							<tr>
+								<td align="left">Fenóis</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+							</tr>
+							<tr>
+								<td align="left">Saponinas</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">+</td>
+								<td align="left">-</td>
+							</tr>
+							<tr>
+								<td align="left">Taninos</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+							</tr>
+							<tr>
+								<td align="left">Esteroides</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+								<td align="left">+</td>
+							</tr>
+							<tr>
+								<td align="left">Alcaloides</td>
+								<td align="left">+</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+							</tr>
+							<tr>
+								<td align="left">Triterpenoides</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+								<td align="left">-</td>
+							</tr>
+						</tbody>
+					</table>
+                    <table-wrap-foot>
+                        <fn id="TFN2">
+                            <p><xref ref-type="table" rid="t2">Table 2</xref>. Phytochemical screening of EEF and EEC of <italic>Senna</italic> Mill. (Fabaceae) species. Present: + Absent: - EEF: Ethanol extract of the leaf. EEC: Ethanol extract from the stem.</p>
+                        </fn>
+                    </table-wrap-foot>
+				</table-wrap>
+			</p>
+			<p>Os metabólitos detectados nas espécies estudadas são consistentes com os metabólitos descritos na literatura para o gênero <italic>Senna</italic>, conhecido por apresentar flavonoides, alcaloides, taninos, esteroides e saponinas em sua composição (<xref ref-type="bibr" rid="B38">Onyegeme-Okerenta <italic>et al.</italic> 2017</xref>, <xref ref-type="bibr" rid="B19">Ishaku <italic>et al.</italic> 2016</xref>, <xref ref-type="bibr" rid="B49">Silva <italic>et al.</italic> 2014</xref>, <xref ref-type="bibr" rid="B51">Sudi <italic>et al</italic>. 2011</xref>, <xref ref-type="bibr" rid="B10">Bukar <italic>et al.</italic> 2009</xref>). É possível perceber que na análise de prospecção química dos extratos houve uma variação de metabólitos secundários. Este fato pode estar atribuído a vários fatores, entre eles estão as diferentes condições ambientais, tais como clima, radiação solar, nutrição mineral, sazonalidade, ritmo circadiano, temperatura, disponibilidade hídrica, e também os tipos de solvente e a metodologia empregada no processo de extração, que podem interferir consideravelmente no conteúdo de praticamente todas as classes de metabólitos secundários (<xref ref-type="bibr" rid="B18">Gomes <italic>et al</italic>. 2016</xref>, <xref ref-type="bibr" rid="B6">Bezerra <italic>et al.</italic> 2013</xref>, <xref ref-type="bibr" rid="B17">Gobbo-Neto &amp; Lopes 2007</xref>).</p>
+            <p>Os teores de fenóis totais apresentaram diferenças significativas entre os extratos etanólicos das diferentes partes e espécies vegetais estudadas (<xref ref-type="table" rid="t3">Tabela 3</xref>). O conteúdo de fenóis totais para os EEF variou de 32,60 ± 0,53 a 184,8 ± 5,09 EAG/g, enquanto que para o EEC foram de 30,03± 1,00 a 191,3 ± 0,47 EAG/g. Os maiores níveis de fenóis totais foram detectados na espécie <italic>S. trachypus</italic>. Os dados da literatura sobre o conteúdo de compostos fenólicos obtidos a partir do extrato aquoso, etanólico e acetona da raiz de <italic>S. alata</italic>, apresentaram uma concentração de fenóis de 46,3, 78,21 e 21,42 mg EAG/g, respectivamente, e de flavonoides de 26,17, 39,29 e 9,65 mg de equivalente de quercetina por grama de extrato (EQ/g), respectivamente (<xref ref-type="bibr" rid="B20">Ita &amp; Ndukwe 2017</xref>). Já o extrato etanólico preparado a partir das folhas de <italic>S. obtusifolia</italic> por <xref ref-type="bibr" rid="B1">Ali <italic>et al</italic>. (2019</xref>), apresentou um teor de fenóis e de flavonoides de 14,39 mg/g e 2,85 mg/g, respectivamente, demonstrando possuir teor de compostos fenólicos inferior ao das mostras de <italic>S. obtusifolia</italic> encontradas no presente estudo. Além disso, o conteúdo de polifenóis encontrado no extrato etanólico e nas frações obtidas a partir das folhas de <italic>S. occidentalis</italic> por <xref ref-type="bibr" rid="B56">Yakubu <italic>et al.</italic> (2018</xref>) variou de 139 mg/mL a 206 mg/mL e de flavonoides de 104 a 142 mg/mL. Já para os extratos preparados a partir das folhas e casca do caule de <italic>S. siamea</italic> revelaram um teor de fenóis totais de 10,21 ± 0,25 g/g e 24,77 ± 0,15 g/g, respectivamente. Por outro lado, o teor de flavonoides foi de 0,08 ± 0,01 g/g para as folhagens, e de 0,04 ± 0,01 g/g para a casca do caule (<xref ref-type="bibr" rid="B25">Kwada &amp; Tella 2009</xref>). Para os extratos etanólicos das folhas e raízes de <italic>S. trachypus</italic> o teor de fenóis totais encontrado foi de 322,09 ± 2,83 EAG/g e de 1277,34 ± 79,54 EAG/g, respectivamente (<xref ref-type="bibr" rid="B49">Silva <italic>et al.</italic> 2014</xref>).<italic>Senna</italic>.</p>
+            <p>
+				<table-wrap id="t3">
+					<label>Table 3.</label>
+					<caption>
+						<title>Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).</title>
+					</caption>
+					<table>
+						<colgroup>
+							<col/>
+							<col span="2"/>
+							<col span="2"/>
+							<col span="2"/>
+						</colgroup>
+						<thead>
+							<tr>
+								<th align="left" rowspan="2">Espécies</th>
+								<th align="center" colspan="2">Fenois<sup>1</sup> mg EAG.g<sup>-1</sup> de extrato </th>
+								<th align="center" colspan="2">DPPH<sup>2</sup> CE<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+								<th align="center" colspan="2"> AChEI<sup>3</sup> CI<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+							</tr>
+							<tr>
+								<th align="center">Média</th>
+								<th align="center">Despad</th>
+								<th align="center">Média</th>
+								<th align="center">Despad</th>
+								<th align="center">Média</th>
+								<th align="center">Despad</th>
+							</tr>
+                        </thead>
+                        <tbody>
+							<tr>
+								<td align="left"><italic>S. alata</italic> (Folhas)</td>
+								<td align="center">53,76 <sup>f</sup></td>
+								<td align="center">± 0,74</td>
+								<td align="center">3,70 <sup>e</sup></td>
+								<td align="center">± 0,04</td>
+								<td align="center">49,42 <sup>f</sup></td>
+								<td align="center">± 0,02</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. alata</italic> (Caule)</td>
+								<td align="center">43,44 <sup>g</sup></td>
+								<td align="center">± 0,21</td>
+								<td align="center">5,41 <sup>c</sup></td>
+								<td align="center">± 0,06</td>
+								<td align="center">53,25 <sup>d</sup></td>
+								<td align="center">± 0,02</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. obtusifolia</italic> (Folhas)</td>
+								<td align="center">76,32 <sup>e</sup></td>
+								<td align="center">± 0,41</td>
+								<td align="center">4,24 <sup>d</sup></td>
+								<td align="center">± 0,06</td>
+								<td align="center">50,37 <sup>e</sup></td>
+								<td align="center">± 0,32</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. obtusifolia</italic> (Caule)</td>
+								<td align="center">86,20 <sup>d</sup></td>
+								<td align="center">± 0,99</td>
+								<td align="center">3,00 <sup>g</sup></td>
+								<td align="center">± 0,05</td>
+								<td align="center">56,90 <sup>c</sup></td>
+								<td align="center">± 0,02</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. occidentalis</italic> (Folhas)</td>
+								<td align="center">32,60 <sup>h</sup></td>
+								<td align="center">± 0,53</td>
+								<td align="center">8,20 <sup>b</sup></td>
+								<td align="center">± 0,07</td>
+								<td align="center">58,76 <sup>b</sup></td>
+								<td align="center">± 0,78</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. occidentalis</italic> (Caule)</td>
+								<td align="center">30,03 <sup>h</sup></td>
+								<td align="center">± 1,00</td>
+								<td align="center">11,19 <sup>a</sup></td>
+								<td align="center">± 0,15</td>
+								<td align="center">57,26 <sup>c</sup></td>
+								<td align="center">± 0,02</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. siamea</italic> (Folhas)</td>
+								<td align="center">51,73 <sup>f</sup></td>
+								<td align="center">± 0,85</td>
+								<td align="center">3,34 <sup>f</sup></td>
+								<td align="center">± 0,05</td>
+								<td align="center">59,77 <sup>a</sup></td>
+								<td align="center">± 0,26</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. siamea</italic> (Caule)</td>
+								<td align="center">111,7 <sup>c</sup></td>
+								<td align="center">± 3,43</td>
+								<td align="center">0,83 <sup>i</sup></td>
+								<td align="center">± 0,01</td>
+								<td align="center">59,52 <sup>ab</sup></td>
+								<td align="center">± 0,15</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. trachypus</italic> (Folhas)</td>
+								<td align="center">184,80 <sup>b</sup></td>
+								<td align="center">± 5,09</td>
+								<td align="center">0,63 <sup>k</sup></td>
+								<td align="center">± 0,01</td>
+								<td align="center">32,40 <sup>g</sup></td>
+								<td align="center">± 0,12</td>
+							</tr>
+							<tr>
+								<td align="left"><italic>S. trachypus</italic> (Caule)</td>
+								<td align="center">191,3 <sup>a</sup></td>
+								<td align="center">± 0,47</td>
+								<td align="center">2,52 <sup>h</sup></td>
+								<td align="center">± 0,03</td>
+								<td align="center">31,44 <sup>h</sup></td>
+								<td align="center">± 0,14</td>
+							</tr>
+							<tr>
+								<td align="left">Quercetina</td>
+								<td align="center">-</td>
+								<td align="center">-</td>
+								<td align="center">1,03 <sup>i</sup></td>
+								<td align="center">± 0,00</td>
+								<td align="center">-</td>
+								<td align="center">-</td>
+							</tr>
+							<tr>
+								<td align="left">Fisiostigmina</td>
+								<td align="center">-</td>
+								<td align="center">-</td>
+								<td align="center">-</td>
+								<td align="center">-</td>
+								<td align="center">1,15 <sup>i</sup></td>
+								<td align="center">± 0,00</td>
+							</tr>
+						</tbody>
+					</table>
+					<table-wrap-foot>
+                        <fn id="TFN3">
+                            <p>Total phenol content, antioxidant activity and acetylcholinesterase enzyme inhibition of <italic>Senna</italic> Mill. (Fabaceae) species. </p>
+                        </fn>
+						<fn id="TFN4">
+							<p>Todas as análises foram realizadas em triplicada e os resultados foram expressos como média ± desvio padrão. As diferenças entre os valores foram examinadas usando análise de variância (ANOVA) e os resultados foram comparados usando o teste de Tukey com 95% nível de confiança. Letras diferentes denotam diferença estatística entre os valores de cada coluna (p &lt; 0,05). <sup>1</sup>Miligrama equivalente ao Ácido Gálico por grama de extrato; <sup>2</sup>Concentração efetiva para inibir 50% do radical livre DPPH (2,2 -difenil-1-picril-hidrazil); <sup>3</sup>Concentração inibitória capaz de inibir 50% da acetilcolinesterase. (-) Testes não realizados.</p>
+						</fn>
+						<fn id="TFN5">
+							<p>All analyzes were performed in triplicate and the results were expressed as mean ± standard deviation. The differences between the values ​​were examined using analysis of variance (ANOVA) and the results were compared using the Tukey test at 95% confidence level. Different letters denote statistical difference between the values ​​of each column (p &lt;0.05). <sup>1</sup> milligram Equivalent to Gallic Acid per gram of extract; <sup>2</sup>Effective concentration to inhibit 50% of the free radical DPPH (2,2 - diphenyl - 1 - picryl - hydrazil); <sup>3</sup>Inhibitory concentration capable of inhibiting 50% of acetylcholinesterase. (-) Tests not performed.</p>
+						</fn>
+					</table-wrap-foot>
+				</table-wrap>
+			</p>
+			<p>Os resultados da atividade antioxidante dos extratos de <italic>Senna</italic> spp. mostraram que os valores de CE<sub>50</sub> para o EEF variaram de 0,63 ± 0,01 a 8,20 ± 0,07 µg/mL, sendo o EEF de <italic>S. trachypus</italic> o que apresentou menor CE<sub>50</sub> com atividade antirradicalar superior ao da quercetina e, portanto, maior potencial antioxidante (<xref ref-type="bibr" rid="B55">Villano <italic>et al</italic>. 2007</xref>). Já para o EEC os valores de CE<sub>50</sub> variaram de 0,83 ± 0,01 a 11,19 ± 0,15 µg/mL (<xref ref-type="table" rid="t3">Tabela 3</xref>). Foi observado que o EEC de <italic>S. siamea</italic> apresentou capacidade antirradicalar próximo à quercetina. Semelhantes aos nossos resultados, estudos anteriores revelaram que as espécies de <italic>S. alata, S. obtusifolia, S. occidentalis, S. siamea</italic> e <italic>S. trachypus</italic>, apresentaram potencial antioxidante e que esta atividade está atribuída à presença de compostos fenólicos (<xref ref-type="bibr" rid="B11">Coelho <italic>et al.</italic> 2017</xref>, <xref ref-type="bibr" rid="B20">Ita &amp; Ndukwe 2017</xref>, <xref ref-type="bibr" rid="B5">Barnaby <italic>et al.</italic> 2016</xref>, <xref ref-type="bibr" rid="B37">Odeja <italic>et al.</italic> 2015</xref>, <xref ref-type="bibr" rid="B49">Silva <italic>et al.</italic> 2014</xref>). </p>
+			<p>Os resultados obtidos na análise de inibição da enzima acetilcolinesterase foram comparados ao do alcaloide fisostigmina que foi o primeiro inibidor descoberto. Os experimentos de inibição da enzima acetilcolinesterase <italic>in vitro</italic> para as espécies de <italic>Senna</italic> produziram apenas resultados com potência moderada (<xref ref-type="table" rid="t3">Tabela 3</xref>). Relatos confirmam a atividade antiacetilcolinesterásica de vários taninos isolados do fruto <italic>Terminalia chebula</italic> Retz.<italic>,</italic> (Combretaceae) que exibiram um efeito de inibição contra a enzima acetilcolinesterase <italic>in vitro</italic> (<xref ref-type="bibr" rid="B22">Kim <italic>et al.</italic> 2018</xref>). Outros compostos, como saponinas, alcaloides e compostos fenólicos, também são relatados na literatura como inibidores da enzima acetilcolinesterase (<xref ref-type="bibr" rid="B40">Paiva <italic>et al</italic>. 2021</xref>, <xref ref-type="bibr" rid="B24">Kozachok <italic>et al</italic>. 2020</xref>, <xref ref-type="bibr" rid="B2">Adedayo <italic>et al</italic>. 2015</xref>). Estas classes de compostos foram detectadas na triagem fitoquímica, embora provavelmente as concentrações nos extratos eram muito baixas para dar resultados satisfatórios no ensaio. Os extratos foliares e do caule de <italic>S. trachypus</italic> apresentaram os valores mais satisfatórios de inibição da enzima acetilcolinesterase, indicando que o isolamento de metabólitos pode levar a potenciais agentes antiacetilcolinesterásicos. Na literatura, não foram encontrados estudos do potencial anticolinesterásico paras as espécies de <italic>Senna</italic> referenciadas, sendo este o primeiro relato de estudo de atividade de inibição para esta enzima. </p>
+			<p>Para os extratos de <italic>Senna</italic> spp., foi observada forte correlação negativa entre os valores de fenóis totais e CE<sub>50</sub> (r = - 0,71), mostrando que quanto maior os teores de fenóis totais, menor a CE<sub>50</sub> e, consequentemente, maior o potencial antioxidante, uma vez que a CE<sub>50</sub> está inversamente relacionada à capacidade antioxidante de um composto (<xref ref-type="bibr" rid="B55">Villano <italic>et al</italic>. 2007</xref>). Dentre os extratos analisados podemos observar na figura 1 o EEF de <italic>S. trachypus.</italic></p>
+			<p>
+				<fig>
+					<label>Figura 1.</label>
+					<caption>
+						<title>Correlação entre o teor de fenóis totais e CE50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+					</caption>
+					<graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf1.jpg"/>
+                    <attrib><xref ref-type="fig" rid="f1">Figure 1</xref>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+				</fig>
+			</p>
+			<p>Na correlação da atividade de inibição da enzima acetilcolinesterase, representada pelo CI<sub>50</sub> com teor de fenóis totais, observou-se uma correlação muito forte (r = -0,84) entre estas duas variáveis, evidenciando que ambas são inversamente proporcionais entre si, ou seja, à medida que o teor de fenóis totais aumenta o valor de CI<sub>50</sub> diminui, como pode ser observado para o EEF de <italic>S. occidentalis</italic> (<xref ref-type="fig" rid="f2">Figura 2</xref>). Isso demonstra que os compostos fenólicos podem ser determinantes nessa atividade, de modo que alguns estudos evidenciaram que flavonoides e outros compostos fenólicos possuem atividade anticolinesterásica (<xref ref-type="bibr" rid="B3">Amessis-Ouchemoukh <italic>et al</italic>. 2014</xref>). </p>
+			<p>
+				<fig id="f2">
+					<label>Figura 2.</label>
+					<caption>
+						<title>Correlação entre o teor de fenóis totais e CI50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+					</caption>
+					<graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf2.jpg"/>
+                    <attrib><xref ref-type="fig" rid="f2">Figure 2</xref>. Correlation between total phenol content and IC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+				</fig>
+			</p>
+			<p>Houve uma correlação moderada (r = 0,43) entre a CI<sub>50</sub> e a CE<sub>50</sub>. Analisando a <xref ref-type="fig" rid="f3">figura 3</xref>, é possível perceber que o EEF e EEC de <italic>S. alata</italic> e EEF de <italic>S. obtusifolia</italic> se destacam no gráfico<italic>,</italic> o que sugere uma grande capacidade dos antioxidantes, como os compostos fenólicos, presentes nos extratos analisados, de atuarem não só através da inibição da acetilcolinesterase (AChEI) mas também por mecanismos de redução de radicais livres.</p>
+			<p>
+				<fig id="f3">
+					<label>Figura 3.</label>
+					<caption>
+						<title>Correlação entre CI50 e a CE50 de espécies de <italic>Senna</italic> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</title>
+					</caption>
+					<graphic xlink:href="2236-8906-hoehnea-49-e1112020-gf3.jpg"/>
+                    <attrib><xref ref-type="fig" rid="f3">Figure 3</xref>. Correlation between IC50 and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</attrib>
+				</fig>
+			</p>
+			<p>Os extratos etanólicos das folhas e caule de <italic>S. alata, S. obtusifolia, S. occidentalis</italic> e <italic>S. siamea,</italic> apresentaram efeito inibitório contra algumas cepas de <italic>T. rubrum</italic>. A maioria dos extratos foram eficazes em diferentes concentrações, com CIM que variaram de 0,07 mg/mL à 2,5 mg/mL e CFM de 0,15 a 5,0 mg/mL contra a grande maioria das cepas fúngicas testadas. Dentre os extratos testados, os de <italic>S. trachypus</italic> foram eficazes contra todas as cepas de <italic>T. rubrum</italic> com CIM que variaram de 0,31 a 0,62 mg/mL e o CFM de 0,62 a 1,25 mg/mL, para ambos os extratos (<xref ref-type="table" rid="t4">Tabela 4</xref>). A presença de compostos fitoquímicos tem sido associada às atividades antimicrobianas da maioria dos materiais vegetais. Algumas classes de metabólitos foram identificadas nesse estudo e podem ser associadas à atividade antimicrobiana (<xref ref-type="bibr" rid="B47">Santos <italic>et al.</italic> 2018</xref>, <xref ref-type="bibr" rid="B37">Odeja <italic>et al.</italic> 2015</xref>). </p>
+			<p>
+				<table-wrap id="t4">
+					<label>Tabela 4. </label>
+					<caption>
+						<title>Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <italic>Senna</italic> Mill. (Fabaceae) frente às espécies de <italic>Trichophyton rubrum</italic>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.</title>
+					</caption>
+					<table>
+						<colgroup>
+							<col/>
+							<col/>
+							<col span="2"/>
+							<col span="2"/>
+							<col span="2"/>
+							<col span="2"/>
+						</colgroup>
+						<thead>
+							<tr>
+								<th align="left" rowspan="4">Espécies</th>
+								<th align="center" rowspan="4">Extrato</th>
+								<th align="center" colspan="2"><italic>T. rubrum</italic></th>
+								<th align="center" colspan="2"><italic>T. rubrum</italic></th>
+								<th align="center" colspan="2"><italic>T. rubrum</italic></th>
+								<th align="center" colspan="2"><italic>T. rubrum</italic></th>
+							</tr>
+							<tr>
+								<th align="center" colspan="2">LABIMIC 5906 </th>
+								<th align="center" colspan="2">LABIMIC 6213 </th>
+								<th align="center" colspan="2">LABIMIC 6205 </th>
+								<th align="center" colspan="2">LABIMIC 6753 </th>
+							</tr>
+							<tr>
+								<th align="center">CIM</th>
+								<th align="center">CFM </th>
+								<th align="center">CIM </th>
+								<th align="center">CFM</th>
+								<th align="center">CIM</th>
+								<th align="center">CFM</th>
+								<th align="center">CIM</th>
+								<th align="center">CFM</th>
+							</tr>
+							<tr>
+								<th align="center" colspan="2">(mg/mL) </th>
+								<th align="center" colspan="2">(mg/mL) </th>
+								<th align="center" colspan="2">(mg/mL) </th>
+								<th align="center" colspan="2">(mg/mL) </th>
+							</tr>
+                        </thead>
+                        <tbody>
+							<tr>
+								<td align="left" rowspan="2"><italic>S. alata</italic></td>
+								<td align="center">EEF</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">2,5</td>
+								<td align="center">5,0</td>
+							</tr>
+							<tr>
+								<td align="center">EEC</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">2,5</td>
+								<td align="center">5,0</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+							</tr>
+							<tr>
+								<td align="left" rowspan="2"><italic>S. obtusifolia</italic></td>
+								<td align="center">EEF</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">2,5</td>
+								<td align="center">5,0</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+							</tr>
+							<tr>
+								<td align="center">EEC</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">1,25</td>
+								<td align="center">2,5</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+							</tr>
+							<tr>
+								<td align="left" rowspan="2"><italic>S. occidentalis</italic></td>
+								<td align="center">EEF</td>
+								<td align="center">0,07</td>
+								<td align="center">0,15</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+							</tr>
+							<tr>
+								<td align="center">EEC</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+							</tr>
+							<tr>
+								<td align="left" rowspan="2"><italic>S. siamea</italic></td>
+								<td align="center">EEF</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+								<td align="center">1,25</td>
+								<td align="center">2,5</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+								<td align="center">1,25</td>
+								<td align="center">2,5</td>
+							</tr>
+							<tr>
+								<td align="center">EEC</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">2,5</td>
+								<td align="center">5,0</td>
+								<td align="center">NI</td>
+								<td align="center">-</td>
+								<td align="center">2,5</td>
+								<td align="center">5,0</td>
+							</tr>
+							<tr>
+								<td align="left" rowspan="2"><italic>S. trachypus</italic></td>
+								<td align="center">EEF</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+							</tr>
+							<tr>
+								<td align="center">EEC</td>
+								<td align="center">0,62</td>
+								<td align="center">1,25</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+								<td align="center">0,31</td>
+								<td align="center">0,62</td>
+							</tr>
+							<tr>
+								<td align="left">Cetoconazol</td>
+								<td align="center"> </td>
+								<td align="center">2,0</td>
+								<td align="center"> </td>
+								<td align="center">1,0</td>
+								<td align="center"> </td>
+								<td align="center">1,0</td>
+								<td align="center"> </td>
+								<td align="center">0,5</td>
+								<td align="center"> </td>
+							</tr>
+						</tbody>
+					</table>
+                    <table-wrap-foot>
+                        <fn id="TFN6">
+                            <p><xref ref-type="table" rid="t4">Table 4</xref>.  Minimum Inhibitory Concentration (MIC) and Minimum Fungicidal Concentration (MFC) of ethanolic extracts (EEs) from <italic>Senna</italic> Mill. LABIMIC: Microbiology Laboratory; EEF: Ethanol extract of the leaf; EEC: Ethanol extract from the stem; NI: It didn't inhibit. (Fabaceae) species compared to <italic>Trichophyton rubrum</italic> species.</p>
+                        </fn>
+                    </table-wrap-foot>
+				</table-wrap>
+			</p>
+			<p>Estudos anteriores realizados com o extrato etanólico da casca do caule de <italic>S. alata</italic> contra fungos dermatofíticos, entre eles espécies de <italic>Trychophyton,</italic> revelou um CIM de 5,0 mg/mL para todos os dermatófitos testados (<xref ref-type="bibr" rid="B52">Sule <italic>et al.</italic> 2011</xref>). A capacidade antifúngica de extratos de diferentes polaridades preparados a partir das folhas de <italic>S. obtusifolia</italic> apresentaram um CIM que variou de 500 a 2000 µg/mL contra diferentes espécies de fungos filamentosos (<xref ref-type="bibr" rid="B13">Doughari <italic>et al.</italic> 2008</xref>). Os resultados obtidos de extratos foliares de polaridades diferentes de <italic>S. occidentalis</italic> revelaram que o extrato metanólico mostrou maior atividade antifúngica entre os demais extratos testados, em uma concentração inibitória mínima de 25 mg/mL (<xref ref-type="bibr" rid="B37">Odeja <italic>et al.</italic> 2015</xref>). Testes utilizando extratos preparados com solventes de diferentes polaridades a partir das folhas de <italic>S. siamea</italic> apresentaram CIM que variaram de 0,032 a 0,128 mg/mL contra o fungo <italic>Cryptococcus gattii</italic> (<xref ref-type="bibr" rid="B36">Nnadi <italic>et al.</italic> 2019</xref>). Na literatura, não foram encontrados estudos do potencial antifúngico para a espécie de <italic>S. trachypus</italic>, sendo este o primeiro registro de atividade antifúngica para a referida espécie. </p>
+			<p>Pesquisas têm revelado que o potencial antifúngico de extratos vegetais está intimamente relacionado, entre outros fatores, com as suas variações quantitativas de compostos fenólicos, dentre eles os flavonoides. Nosso estudo confirmou que as espécies estudadas possuem propriedades antifúngicas, e que seus efeitos sobre os dermatófitos fundamentam-se em seus teores de compostos fenólicos encontrados, e os demais outros metabólitos secundários aqui não estudados. Os efeitos antifúngicos atribuídos aos compostos fenólicos podem resultar na ruptura da membrana celular, ou ainda, inibir a divisão celular e o desenvolvimento das hifas por meio de genes específicos, além de interferir nas vias metabólicas e/ou induzir a apoptose por perturbar a homeostase redox (<xref ref-type="bibr" rid="B26">Lagrouh <italic>et al.</italic> 2017</xref>, <xref ref-type="bibr" rid="B31">Mohamed <italic>et al.</italic> 2017</xref>).</p>
+			<p>Foram detectados, nos EEF e EEC das espécies de <italic>Senna</italic>, a presença de metabólitos secundários, alto teor de fenóis totais e capacidade antioxidante para todas as espécies, em especial <italic>S. trachypus</italic>. Para a atividade anticolinesterase apenas a espécie de <italic>S. trachypus</italic> manifestou uma melhor ação inibitória. Nas condições experimentais utilizadas, evidenciou-se atividade antifúngica das espécies frente a maioria dos dermatófitos testados, em especial os extratos de <italic>S. trachypus</italic>. Foi observada também correlação forte, muito forte e moderada entre as variáveis fenóis totais e atividade antioxidante, fenóis totais e antiacetilcolinesterase e atividade antioxidante e antiacetilcolinesterase, respectivamente<italic>.</italic> Os resultados apontam que <italic>S. trachypus</italic>, espécie endêmica da Caatinga, é a mais promissora entre todas as plantas estudadas, representando uma fonte potencial para a obtenção de compostos químicos úteis para estudos clínicos e farmacológicos, visando o desenvolvimento de novos agentes farmacológicos naturais. </p>
+		</sec>
+	</body>
+	<back>
+		<ack>
+			<title>Agradecimentos</title>
+			<p>Os autores agradecem a Universidade Estadual do Ceará (UECE) e a Universidade Estadual Vale do Acaraú (UVA) pelo apoio técnico, e a Fundação Cearense de Apoio ao Desenvolvimento Científico e Tecnológico (FUNCAP) pelo apoio financeiro concedido (processos PBI3-0139-00252.01.00/18; BP4-0172-00170.01.00/20). </p>
+		</ack>
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+							<surname>Villano</surname>
+							<given-names>D.</given-names>
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+						<name>
+							<surname>Fernandez-Pachón</surname>
+							<given-names>M.S.</given-names>
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+							<surname>Moya</surname>
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+							<surname>Troncoso</surname>
+							<given-names>A.M.</given-names>
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+						<name>
+							<surname>García-Parrilla</surname>
+							<given-names>M.C.</given-names>
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+					<year>2007</year>
+					<article-title>Radical scavenging ability of polyphenolic compounds towards DPPH free radical</article-title>
+					<source>Talanta</source>
+					<volume>71</volume>
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+</article>
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+<span class="_articleBadge">Artigo</span><span class="_separator"> • </span><span class="_editionMeta">Hoehnea 49 <span class="_separator"> • </span>2022</span><span class="_separator"> • </span><span class="group-doi"><a href="https://doi.org/10.1590/2236-8906-111/2020" class="_doi" target="_blank">https://doi.org/10.1590/2236-8906-111/2020</a>
+         
+        <a class="copyLink" data-clipboard-text="https://doi.org/10.1590/2236-8906-111/2020"><span class="sci-ico-link"></span>copiar</a></span>
+</div>
+<h1 class="article-title">
+<span class="sci-ico-openAccess showTooltip" data-toggle="tooltip" data-original-title="by 4.0 "></span>Prospecção química, atividade antioxidante, anticolinesterásica e antifúngica de extratos etanólicos de espécies de <i>Senna</i> Mill. (Fabaceae)<a id="shorten" href="#" class="short-link"><span class="sci-ico-link"></span></a>
+</h1>
+<h2 class="article-title">Chemical prospecting and antioxidant, anticholinesterase and antifungal activity of ethanol extracts from <i>Senna</i> Mill. species. (Fabaceae)</h2>
+<div class="articleMeta"></div>
+<div class="contribGroup">
+<span class="dropdown"><a id="contribGroupTutor1" class="dropdown-toggle" data-toggle="dropdown"><span> Andréa Maria Neves </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor1">
+<strong></strong> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil<div class="corresp">
+					<h3><sup>4</sup></h3> Autor para correspondência: <a href="mailto:andreamarianeves@gmail.com">andreamarianeves@gmail.com</a>
+				</div>
+<a href="http://orcid.org/0000-0002-7388-1844" class="btnContribLinks orcid">http://orcid.org/0000-0002-7388-1844</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor2" class="dropdown-toggle" data-toggle="dropdown"><span> Selene Maia de Morais </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor2">
+<strong></strong> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil<a href="http://orcid.org/0000-0002-2766-3790" class="btnContribLinks orcid">http://orcid.org/0000-0002-2766-3790</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor3" class="dropdown-toggle" data-toggle="dropdown"><span> Hélcio Silva dos Santos </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor3">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Exatas e Tecnologia, Curso de Química, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0001-5527-164X" class="btnContribLinks orcid">http://orcid.org/0000-0001-5527-164X</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor4" class="dropdown-toggle" data-toggle="dropdown"><span> Marcílio Matos Ferreira </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor4">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0003-2503-9772" class="btnContribLinks orcid">http://orcid.org/0000-0003-2503-9772</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor5" class="dropdown-toggle" data-toggle="dropdown"><span> Ricardo Carneiro Vera Cruz </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor5">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-2035-0425" class="btnContribLinks orcid">http://orcid.org/0000-0002-2035-0425</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor6" class="dropdown-toggle" data-toggle="dropdown"><span> Elnatan Bezerra de Souza </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor6">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-5222-4378" class="btnContribLinks orcid">http://orcid.org/0000-0002-5222-4378</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor7" class="dropdown-toggle" data-toggle="dropdown"><span> Lúcia Betânia da Silva Andrade </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor7">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-4384-5738" class="btnContribLinks orcid">http://orcid.org/0000-0002-4384-5738</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor8" class="dropdown-toggle" data-toggle="dropdown"><span> Raquel Oliveira dos Santos Fontenelle </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor8">
+<strong></strong> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil<a href="http://orcid.org/0000-0002-8865-5954" class="btnContribLinks orcid">http://orcid.org/0000-0002-8865-5954</a>
+</ul></span><a href="" class="outlineFadeLink" data-toggle="modal" data-target="#ModalTutors">Sobre os autores</a>
+</div>
+<div class="row">
+<ul class="col-md-2 hidden-sm articleMenu"></ul>
+<article id="articleText" class="col-md-10 col-md-offset-2 col-sm-12 col-sm-offset-0"><div class="articleSection" data-anchor="RESUMO">
+<h1 class="articleSectionTitle">RESUMO</h1>
+<p>O objetivo deste trabalho foi avaliar o perfil químico, teor de fenóis totais e as atividades antioxidante, antiacetilcolinesterásica e antifúngica dos extratos etanólicos das folhas (EEF) e do caule (EEC) de cinco espécies de <i>Senna</i>, bem como avaliar a correlação entre o conteúdo de fenóis totais com a atividade sequestradora do radical livre DPPH e com a inibição da enzima acetilcolinesterase AChEI. No teste fitoquímico, evidenciou-se a presença de metabólitos secundários em todos os extratos. Os EEF e EEC de <i>Senna trachypus</i>, destacaram-se por apresentar os maiores valores de fenóis totais. Os EEF e EEC de <i>S. trachypus</i> mostraram a melhor ação sobre a enzima acetilcolinesterase. Todas as espécies apresentaram atividade antioxidante, em especial o EEF de <i>S. trachypus</i>. Foi observado correlação forte para as variáveis fenóis totais e atividade antioxidante (r = -0,71), muito forte para fenóis totais e antiacetilcolinesterase (r = -0,84) e atividade moderada para atividade antioxidante e antiacetilcolinesterase (0,43). Apenas os extratos de <i>S. trachypus</i> apresentaram atividade contra todos os dermatófitos, quando comparado às demais espécies. A espécie <i>S. trachypus</i> foi considerada a planta mais promissora para estudos subsequentes, a fim de encontrar compostos com ações farmacológicas. </p>
+<p><strong>Palavras-chave:</strong><br>acetilcolinesterase; dermatófitos; fitoquímica; produtos naturais; radicais livres</p>
+</div>
+<div class="articleSection" data-anchor="ABSTRACT">
+<h1 class="articleSectionTitle">ABSTRACT</h1>
+<p>The objective of this work was to evaluate the chemical profile, total phenol content and the antioxidant, antiacetylcholinesterase and antifungal activities of ethanol extracts from leaves (EEF) and stem (EEC) of five species of <i>Senna</i>, as well as to evaluate the correlation between the content of total phenols with the DPPH free radical scavenging activity and with the inhibition of the acetylcholinesterase AChEI enzyme. The phytochemical test showed the presence of secondary metabolites in all extracts. The EEF and EEC of <i>Senna trachypus</i>, stood out for presenting the highest values of total phenols. <i>S. trachypus</i> EEF and EEC showed the best action on the acetylcholinesterase enzyme. All species showed antioxidant activity, especially the EEF from <i>S. trachypus</i>. A strong correlation was observed for the variables total phenols and antioxidant activity (r = -0.71), very strong for total phenols and anti-acetylcholinesterase (r = -0.84) and moderate activity for antioxidant and anti-acetylcholinesterase activity (r = 0.43). Only <i>S. trachypus</i> extracts showed activity against all dermatophytes, when compared to the other species. The species <i>S. trachypus</i> was considered the most promising plant for further studies, in order to find compounds with pharmacological actions.</p>
+<p><strong>Keywords:</strong><br>acetylcholinesterase; dermatophytes; phytochemistry; natural products; free radicals</p>
+</div>
+<div class="articleSection" data-anchor="Text">
+<h1 class="articleSectionTitle">Introdução</h1>
+<p><i>Senna</i> Mill. é um gênero monofilético com distribuição pantropical e ampla variedade morfológica (<span class="ref"><strong class="xref xrefblue">Pellerin <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Pellerin, R.J., Waminal, N.E. &amp; Kim, H.H. 2019. FISH mapping of rDNA and telomeric repeats in 10 Senna species. Horticulture, Environment, and Biotechnology 60: 253-260.</span></span></span>). Possuindo aproximadamente 300 espécies, das quais 200 nas Américas, este gênero é o segundo maior da família Fabaceae (<span class="ref"><strong class="xref xrefblue">Queiroz 2009</strong><span class="refCtt closed"><span>Queiroz, L.P. 2009. Leguminosas da Caatinga. Universidade Estadual de Feira de Santana, Feira de Santana, 467 p.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kim <i>et al</i>. 2018</strong><span class="refCtt closed"><span>Kim, M.S., Lee, D.Y., Sung, S.H. &amp; Jeon, W.K. 2018. Anti-cholinesterase activities of hydrolysable tannins and polyhydroxytriterpenoid derivatives from Terminalia chebula Retz. fruit. Fruit Rec Nat Prod 12: 284-289.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Souza &amp; Silva 2016</strong><span class="refCtt closed"><span>Souza, A.O. &amp; Silva, M.J. 2016. Senna (Leguminosae, Caesalpinioideae) na Floresta Nacional de Silvânia, Goiás, Brasil. Rodriguésia 67: 773-784. </span></span></span>). O gênero é representado no Brasil por 79 espécies, onde 29 são endêmicas, sendo a região Nordeste a que apresenta a maior riqueza de espécies com 53 registros (<span class="ref"><strong class="xref xrefblue">BFG 2018</strong><span class="refCtt closed"><span>BFG. 2018. Brazilian Flora 2020: Innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 1513-1527. </span></span></span>). </p>
+<p>Trata-se de um gênero muito expressivo na flora do semiárido, alcançando destaque no Domínio Fitogeográfico da Caatinga, onde são catalogadas 42 espécies (<span class="ref"><strong class="xref xrefblue">Souza &amp; Bortoluzzi 2015</strong><span class="refCtt closed"><span>Souza, V.C.; Bortoluzzi, R.L.C. 2015. Senna in Lista de Espécies da Flora do Brasil. Jardim Botânico do Rio de Janeiro. </span></span></span>). As espécies de <i>Senna</i> são geralmente arbustos ou arvoretas, raramente ervas ou subarbustos anuais. Entre as suas características diagnósticas estão os nectários extraflorais convexos, interfoliolares, flores vistosas, com pétalas amarelo-brilhantes, anteras amarelas, rígidas, com deiscência abrindo por poros ou fendas, ausência de bractéolas no pedicelo, frutos deiscentes plano-compressos ou indeiscentes e cilíndricos (<span class="ref"><strong class="xref xrefblue">Queiroz 2009</strong><span class="refCtt closed"><span>Queiroz, L.P. 2009. Leguminosas da Caatinga. Universidade Estadual de Feira de Santana, Feira de Santana, 467 p.</span></span></span>).</p>
+<p>As espécies de <i>Senna</i> têm diversas aplicações medicinais e são eficazes no tratamento para uma série de doenças, como malária, micose, dengue, eczema, hepatite e dermatite, sendo também indicadas como anti-hipertensivo, vermífugo, laxante, abortivo e antitussígeno (<span class="ref"><strong class="xref xrefblue">Macedo <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Macedo, E.M., Alan, J.G., &amp; Silva, M.G.V. 2016. Quimiodiversidade e propriedades biofarmacológicas de espécies de Senna nativas do Nordeste do Brasil. Revista Virtual de Química 8: 169-195.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bieski <i>et al</i>. 2015</strong><span class="refCtt closed"><span>Bieski, I.G.C., Leonti, M., Arnason, J.T., Ferrier, J., Rapinski, M., Violante, I.M.P., Balogun,S.O., Pereira, J.F.C.A., Figueiredo, R.D.C.F., Lopes, C.R.A.S., Silva, D.R.D., Pacini, A., Albuquerque, U.P. &amp; Martins, D.T.D.O. 2015. Ethnobotanical study of medicinal plants by population of valley of Juruena region, legal amazon, Mato Grosso, Brazil. Journal of Ethnopharmacology 173: 383-423.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kabir <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Kabir, M.H., Hasan, N., Rahman, M.M., Rahman, M.A., Khan, J.A., Hoque, N.T., Bhuiyan, M.R.Q., Mou, S.M.; Jahan, R. &amp; Rahmatullah, M. 2014. A survey of medicinal plants used by the Deb barma clan of the Tripura tribe of Moulvibazar district, Bangladesh. Journal of Ethnobiology and Ethnomedicine 10: 1-19.</span></span></span>). Além de suas aplicações farmacológicas, estudos têm revelado que espécies pertencentes a este gênero possuem, em sua composição, uma vasta diversidade de princípios bioativos que estão associadas a diferentes atividades biológicas. Neste sentido, podemos citar como exemplo as atividades antioxidantes, antitumoral, antibacterianas, antifúngicas e anti-inflamatórias (<span class="ref"><strong class="xref xrefblue">Neves <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Neves, A.M., Costa, O.S., Coutinho, M.G.S., Souza, E.B., Santos, H.S., Silva, M.G.V. &amp; Fontenelle, R.O.S. 2017. Caracterização química e o potencial antimicrobiano de espécies do gênero Senna Mill (Fabaceae). Rev. Virtual Quim 9: 2506-2538.</span></span></span>).</p>
+<p>As plantas são fontes alternativas promissoras de substâncias de interesse biológico e farmacológico, já que podem produzir, a partir de seu metabolismo secundário, uma enorme diversidade de substâncias, dentre estas, os compostos fenólicos. Alguns estudos têm revelado que os compostos fenólicos são responsáveis por várias atividades biológicas, incluindo atividade antifúngica. Esta atividade pode ser direta nos micro-organismos, ou sobre outros fatores necessários para a expressão da virulência ou patogenicidade (<span class="ref"><strong class="xref xrefblue">Rodrigues <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Rodrigues, F.C., Dos Santos, A.T.L., Machado, A.J.T., Bezerra, C.F., de Freitas, T.S., Coutinho, H.D.M., Morais-Braga, M.F.B., Bezerra, J.W.A., Duarte, A.E., Kamdem, J.P., Boligon, A.A., Campos, M.M.A., Barros, L.M. 2019. Chemical composition and anti-Candida potencial of the extracts of Tarenaya spinosa (Jacq.) Raf.(Cleomaceae). Comparative immunology, microbiology and infectious diseases 64: 14-19.</span></span></span>).</p>
+<p>Os compostos fenólicos estão entre os metabólitos secundários mais estudados, notadamente por possuírem grande potencial para atividades antioxidantes, atuando na redução do risco de algumas doenças agudas e crônicas relacionadas ao estado redox do corpo humano, ocasionadas pelos radicais livres. Estas moléculas apresentam uma alta capacidade reativa, sendo consideradas perigosas para os organismos vivos, causando doenças prejudiciais, incluindo doenças neurodegenerativas, como o mal de Alzheimer (DA). Atualmente, uma das teorias mais aceitas na abordagem padrão no tratamento sintomático dessa demência é a “hipótese colinérgica”. Portanto, os inibidores da enzima acetilcolinesterase (AChEI) preservam os níveis de acetilcolina, melhorando a eficiência da transmissão colinérgica (<span class="ref"><strong class="xref xrefblue">Bardakci <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Bardakci, H., CeleP, E., Gözet, T., Kan, Y. &amp; Kirmizibekmez, H. 2019. Phytochemical characterization and antioxidant activities of the fruit extracts of several Crataegus taxa. South African Journal of Botany 124: 5-13. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Lim <i>et al</i>. 2019</strong><span class="refCtt closed"><span>Lim, S., Choi, A.H., Kwon, M., Joung, E.J., Shin, T., Lee, S.G., Kim, NG. &amp; Kim, H. R. 2019. Evaluation of antioxidant activities of various solvent extract from Sargassum serratifolium and its major antioxidant components. Food Chemistry 278: 178-184.</span></span></span>; <span class="ref"><strong class="xref xrefblue">Neagu <i>et al</i>. 2016</strong><span class="refCtt closed"><span>Neagu, E., Radu, G.L., Albu, C., &amp; Paun, G. 2016. Antioxidant activity, acetylcholinesterase and tyrosinase inhibitory potential of Pulmonaria officinalis and Centarium umbellatum extracts. Saudi Journal of Biological Sciences, 3: 578-585.</span></span></span>).</p>
+<p>Por este motivo, a utilização de dietas ricas ou enriquecidas com antioxidantes podem prevenir, ou pelo menos amenizar, a deterioração orgânica por um excessivo estresse oxidativo. Além disso, o crescimento sobre a investigação científica envolvendo os efeitos antioxidantes de extratos brutos, frações purificadas, ou mesmo de compostos isolados, onde estão classificados os compostos fenólicos, são demonstrados em muitos estudos (<span class="ref"><strong class="xref xrefblue">Penido <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Penido, A.B., De Morais, S.M., Ribeiro, A.B., Alves, D.R., Rodrigues, A.L.M., dos Santos, L.H. &amp; de Menezes, J.E.S.A. 2017. Medicinal plants from northeastern Brazil against Alzheimer’s disease. Evidence-Based Complementary and Alternative Medicine 2017: 1-7. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Morais <i>et al.</i> 2013</strong><span class="refCtt closed"><span>Morais, S.M., Lima, K.S.B., Siqueira, S.M.C., Cavalcanti, E.S.B., Souza, M.S.T., Menezes, J.E.S.A., Trevisan, M.T.S. 2013. Correlação entre as atividades antiradical, antiacetilcolinesterase e teor de fenóis totais de extratos de plantas medicinais de farmácias vivas. Revista Brasileira de Plantas Medicinais 15: 575-582. </span></span></span>).</p>
+<p>Desta forma, investigar a atividade antifúngica e anticolinesterásica de extratos de espécies de <i>Senna</i>, analisando o seu potencial antioxidante, o seu teor de fenóis totais e o seu perfil fitoquímico, são maneiras de promover tanto o conhecimento acerca dessas espécies, como também potencializar o descobrimento de novos fitofármacos para o combate de inúmeras enfermidades. Assim, este trabalho avaliou o perfil fitoquímico, o teor de fenóis totais e as atividades antioxidante, anticolinesterásica e antifúngica dos extratos etanólicos de <i>S. alata</i> (L.) Roxb., <i>S. obtusifolia</i> (L.) H.S.Irwin &amp; Barneby, <i>S. occidentalis</i> (L.) Link, <i>S. siamea</i> (Lam.) H.S.Irwin &amp; Barneby e <i>S. trachypus</i> (Benth.) H.S.Irwin &amp; Barneby, e a correlação entre o teor de fenóis totais e as atividades antioxidante e anticolinesterásica. </p>
+<h1 class="articleSectionTitle">Materiais e métodos</h1>
+<p>Material vegetal e preparação dos extratos - Foram selecionadas para este estudo cinco espécies de <i>Senna</i>, sendo uma exótica naturalizada e quatro nativas, das quais uma é endêmica do Brasil, ocorrendo no Cerrado e na Caatinga (<span class="ref"><strong class="xref xrefblue">BFG 2018</strong><span class="refCtt closed"><span>BFG. 2018. Brazilian Flora 2020: Innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 1513-1527. </span></span></span>) (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>Tabela 1</a>). As folhas e caules de <i>Senna</i> spp. foram coletados em diferentes locais da região Noroeste do Ceará. A identificação botânica das espécies foi realizada no Herbário Francisco José de Abreu Matos da Universidade Estadual Vale do Acaraú (HUVA), pelo professor Dr. Elnatan Bezerra de Souza. Para o preparo dos extratos, 200g das folhas e caule secos de cada espécie de um mesmo indivíduo foram triturados e imersos durante 10 dias em 500 mL de etanol e, na sequência o extrato foi filtrado e concentrado em um evaporador rotativo a (60°C) durante 2 h. Após este processo, foi mantido em banho-maria (40°C) até a eliminação total do solvente, obtendo-se o extrato etanólico das folhas (EEF) e extrato etanólico do caule (EEC) (<span class="ref"><strong class="xref xrefblue">Matos 2009</strong><span class="refCtt closed"><span>Matos, F.J.A. 2009. Introdução à Fitoquímica Experimental. 3 ed. Fortaleza: UFC. 150p.</span></span></span>).</p>
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+<strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
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+<p>Triagem fitoquímica - Os extratos etanólicos foram submetidos a triagem fitoquímica, tomando como referência a metodologia descrita por <span class="ref"><strong class="xref xrefblue">Matos (2009</strong><span class="refCtt closed"><span>Matos, F.J.A. 2009. Introdução à Fitoquímica Experimental. 3 ed. Fortaleza: UFC. 150p.</span></span></span>). Através deste ensaio preliminar, foi possível verificar as principais classes de metabólitos secundários por meio de reações químicas que resultaram no aparecimento de coloração e/ou precipitado, característico para cada classe de substância. Os ensaios foram conduzidos para as seguintes classes de substâncias: fenóis, taninos, flavonoides, saponinas, esteroides, triterpenoides e alcaloides. Todos os testes foram realizados em triplicata procedimentais. </p>
+<p>Determinação do teor de fenóis totais - O teor de fenóis totais nos extratos etanólicos foi determinado pelo método espectrofotométrico de Folin-Ciocateau, utilizando ácido gálico como padrão de referência (<span class="ref"><strong class="xref xrefblue">Kim <i>et al.</i> 2006</strong><span class="refCtt closed"><span>Kim, K.H., Tsao, R., Yang, R. &amp; Cui, S.W. 2006. Phenolic acid profiles and antioxidant activities of wheat bran extracts and the effect of hydrolysis conditions. Food Chemistry 95: 466-473.</span></span></span>). Em cada tubo adicionou-se 0,2 mL de cada extrato nas concentrações (0,62; 0,31 e 0,15 mg mL<sup>-1</sup>) com 1 mL do reagente Folin-Ciocalteau agitado por 2 minutos e adicionado 0,8 mL de carbonato de sódio (Na<sub>2</sub>CO<sub>3</sub>) 7,5% (m/v). Para o tubo controle foi utilizado 1 mL do reagente Folin- Ciocalteau com 0,8 mL de Na<sub>2</sub>CO<sub>3</sub> e 0,2 mL de etanol, em triplicata. Os tubos foram deixados em banho-maria a 37 ̊C por 30 minutos na ausência de luz. Logo em seguida, foi realizado a leitura dos tubos em comprimento de onda de 765 nm. O teor de fenóis foi calculado e expresso em mg de equivalente de ácido gálico por grama de extrato (EAG.g<sup>-1</sup>), com base numa curva padrão preparada com ácido gálico. Todos os testes foram realizados em triplicata.</p>
+<p>Atividade antioxidante - A atividade antioxidante dos extratos foi determinada pelo método de redução do radical 2,2’-difenil-1-picril-hidrazil (DPPH), segundo a metodologia modificada por <span class="ref"><strong class="xref xrefblue">Brand-Williams <i>et al.</i> (1995</strong><span class="refCtt closed"><span>Brand-Williams, W., Cuvelier, M.E. &amp; Berset, C.L.W.T. 1995. Use of a free radical method to evaluate antioxidant activity. LWT-Food Science and Technology 1: 25-30.</span></span></span>), <span class="ref"><strong class="xref xrefblue">Sanchez-Moreno <i>et al</i>. (1998</strong><span class="refCtt closed"><span>Sánchez‐Moreno, C., Larrauri, J.A. &amp; Saura‐Calixto, F. 1998. A procedure to measure the antiradical efficiency of polyphenols. Journal of the Science of Food and Agriculture 76: 270-276.</span></span></span>). Foram preparadas soluções etanólicas das amostras nas concentrações de 5,0; 2,5; 1,25; 0,62; 0,31 e 0,15 mg mL<sup>-1</sup>. Foram utilizados 100 µL dos extratos com 2,4 mL de DPPH (0,04 mg mL<sup>-1</sup>). Para o tubo controle foram utilizados 100 µL de etanol com 2,4 mL de DPPH em triplicata. O meio reacional ficou por 30 minutos na ausência da luz, e posteriormente foi realizada a leitura em comprimento de onda 515 nm. A atividade sequestradora do radical DPPH pelos extratos nas diferentes concentrações foi calculada pela expressão do índice de varredura em porcentagem (IV%): IV% = (Abs <sub>DPPH</sub> - Abs <sub>Amostra</sub> / Abs <sub>DPPH</sub>) x 100. A concentração efetiva para inibir 50% do radical livre DPPH (CE<sub>50</sub>) foi obtida com auxílio do Software Excel 2019, onde, a partir dos valores das concentrações finais da amostra e o índice de varredura (IV%), foram originados gráficos de dispersão cujas equações das retas foram utilizadas para se obter os valores da média e desvio padrão. Para fins de comparação, foi construída uma curva de calibração com diferentes porcentagens do flavonoide quercetina, que apresenta elevada atividade antioxidante em radical livre DPPH.</p>
+<p>Avaliação da atividade anticolinesterásica <i>in vitro</i> - O ensaio para verificação da inibição da enzima acetilcolinesterase (AChE) dos extratos foi realizado de acordo com a metodologia descrita por <span class="ref"><strong class="xref xrefblue">Ellman <i>et al.</i> (1961</strong><span class="refCtt closed"><span>Ellman, G.L., Courtney, K.D., Andres Jr, V. &amp; Featherstone, R.M. 1961. A new and rapid colorimetric determination of acetylcholinesterase activity. Biochemical Pharmacology: 7: 88-95.</span></span></span>). Em placas estéreis de 96 poços, foram adicionados 25 µL de iodeto de acetiltiocolina (15 mM), 125 µL de 5,5’-ditiobis-[2-nitrobenzóico] na solução Tris/HCL (50 nM, pH 8, com 0,1 M de NaCL e 0,02 M de MgCL<sub>2</sub> .6H<sub>2</sub>O. (3 mM, DTNB ou reagente de Ellman)), 50 µL da solução Tris/HCL (50 nM, pH 8, com 0,1% de albumina sérica bovina (BSA) e 25 µL dos extratos de <i>Senna</i> spp. na concentraçao de 0,2 mg.mL<sup>-1</sup> em tampão Tris/HCL (50 mM, pH 8) de 0,2 mg.mL<sup>-1</sup> (<span class="ref"><strong class="xref xrefblue">Rhee <i>et al.</i> 2001</strong><span class="refCtt closed"><span>Rhee, I.K., van de Meent, M., Ingkaninan, K. &amp; Verpoorte, R. 2001. Screening for acetylcholinesterase inhibitors from Amaryllidaceae using silica gel thin-layer chromatography in combination with bioactivity staining. Journal of Chromatography A 915: 217-223.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Trevisan <i>et al.</i> 2003</strong><span class="refCtt closed"><span>Trevisan, M.T.S., Macedo, F.V.V., Meent, M.V.D., Rhee, I.K. &amp; Verpoorte, R. 2003. Seleção de plantas com atividade anticolinesterase para tratamento da doença de Alzheimer. Química Nova 26: 301-304.</span></span></span>). </p>
+<p>A absorbância foi aferida a 405 nm durante 30 segundos. Em seguida, foram adicionados 25 µL da enzima acetilcolinesterase (0,25 U.mL<sup>-1</sup>) e a absorbância foi aferida por minuto até o total de 25 minutos de incubação da enzima. Como padrão negativo foram utilizadas todas as soluções, excetuando-se a amostra. O padrão utilizado como controle positivo foi a fisostigmina (0,22 mg.mL<sup>-1</sup>.) e todas as amostras foram analisadas em triplicata. A atividade anticolinesterásica dos extratos vegetais foi determinada de acordo com os valores de CI<sub>50</sub> (Concentração inibitória capaz de inibir 50% da enzima acetilcolinesterase) como: alta potência (CI<sub>50</sub> &lt; 20 μg. mL<sup>-1</sup>); potência moderada (20 &lt; CI<sub>50</sub> &lt; 200 μg.mL<sup>-1</sup>) e baixa potência (200 &lt; CI<sub>50</sub> &lt; 1000 μg.mL<sup>-1</sup>) (<span class="ref"><strong class="xref xrefblue">Santos <i>et al</i>. 2018</strong><span class="refCtt closed"><span>Santos, G.H.F., Amaral, A. &amp; Da Silva, E.B. 2018. Antibacterial activity of irradiated extracts of Anacardium occidentale L. on multiresistant strains of Staphylococcus aureus. Applied Radiation and Isotopes 140: 327-332.</span></span></span>).</p>
+<p>Ensaio antifúngico <i>in vitro</i> - No ensaio para verificação da concentração inibitória mínima (CIM) dos EE das espécies de <i>Senna</i>, foram utilizadas cepas de <i>Trichophyton rubrum</i> obtidas a partir da micoteca da Universidade Federal de Pernambuco e do Centro Especializado de Micologia Médica (CEMM) da Universidade Federal do Ceará<i>.</i> Para este ensaio foi utilizado o método de microdiluição em caldo<i>,</i> de acordo com a metodologia descrita por (<span class="ref"><strong class="xref xrefblue">Neves <i>et al.</i> 2019</strong><span class="refCtt closed"><span>Neves, A.M., Silva, H.S., Souza, E.B., Fontenelle, R.O.S., Silva, A.C.S., Morais, S.M. 2019. Perfil fitoquímico e avaliação da atividade antifúngica da fração hexânica de Mitracarpus baturitensis (Rubiaceae). Essentia 20: 96-101. </span></span></span>) com as normas do protocolo <span class="ref"><strong class="xref xrefblue">Clinical Laboratory Standards Insitute do documento M38-A (CLSI M38-A2, 2008</strong><span class="refCtt closed"><span>Clinical and Laboratory Standards Institute. 2008. Reference Method for Broth Dilution Antifungal Susceptibility Testing of Filamentous Fungi (Approved Standard Document M38. CLSI), vol. M38-A2, Second ed. Clinical and Laboratory Standards Institute, Wayne, PA.</span></span></span>)<i>.</i> Em placas de 96 poços estéreis, foram adicionados 100 µL de meio RPMI em todos os poços e 10 mg mL<sup>-1</sup> dos extratos de <i>Senna</i> spp. foi acrescentado a todos os poços da primeira coluna e, em sequência foram efetuadas as diluições seriadas. Finalmente, 100 µL do inóculo foi adicionado aos poços da placa. Como controle foi utilizado o Cetoconazol (Sigma, Chemical Co., USA). Para as análises de susceptibilidade, os extratos etanólicos foram testados em concentrações variando de 0,002 a 2,5 mg mL<sup>-1</sup>. As placas foram cobertas com parafilme e incubadas a 37 °C e a leitura visual foi realizada após cinco dias para <i>T. rubrum</i>. Procedimento realizado em duplicata. A CIM é definida como a menor concentração do extrato capaz de inibir 100% do crescimento fúngico visível (<span class="ref"><strong class="xref xrefblue">Fontenelle <i>et al.</i> 2007</strong><span class="refCtt closed"><span>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Kerntopf, M.R., Brilhante, R.S.N., Cordeiro, R.A., Tomé, A.R., Queiroz, M.G.R., Nascimento, N.R.F. &amp; Sidrim, J.J.C. 2007. Chemical composition, toxicological aspects and antifungal activity of essential oil from Lippia sidoides Cham. Journal of Antimicrobial Chemotherapy 59: 934-940. </span></span></span>). A concentração fungicida mínima (CFM) foi determinada por subcultura de 100 μL da solução de poços sem turbidez no meio Ágar Dextrose de Batata, a 28 °C. (<span class="ref"><strong class="xref xrefblue">Fontenelle <i>et al.</i> 2008</strong><span class="refCtt closed"><span>Fontenelle, R.O.S., Morais, S.M., Brito, E.H.S., Brilhante, R.S.N., Cordeiro, R.A., Nascimento, N.R.F., Kerntopf, M.R., Sidrim, J.J.C. &amp; Rocha, M.F.G. 2008. Antifungal activity of essential oils of Croton species from the Brazilian caatinga biome. Journal of Applied Microbiology 104: 1383-1390.</span></span></span>).</p>
+<p>Análise estatística - Todas as determinações foram realizadas em triplicata e todos os resultados foram apresentados como média ± desvio-padrão (DP). Foram realizadas análises de variância (ANOVA) com duas repetições e o Teste Tukey, ao nível de significância de 5%, usando programa Graph Pad Prism<sup>®</sup> v5.01 (GraphPadSoftware, San Diego, CA, E.U.A.). As diferenças entre as médias foram consideradas significativas quando o valor obtido para "<i>p</i>" foi menor que 0,05 (<i>p</i> &lt; 0,05). </p>
+<p>Para análises da correlação entre os dados, foi utilizado o coeficiente de correlação de Pearson no software Microsoft Excel 2019, a qual mede o grau da correlação linear entre duas variáveis quantitativas. A intensidade dessa correlação é dada pelo “r”, que é um índice adimensional com valores situados entre -1,0 e 1,0. Quando o valor de r estiver entre 0,00-0,19 a correlação é muito fraca; entre 0,20-0,39 é fraca; 0,40-0,59 é uma correlação moderada; entre 0,60-0,79 é forte e finalmente entre 0,80-1,0 diz-se que é uma correlação muito forte (<span class="ref"><strong class="xref xrefblue">Mukaka 2012</strong><span class="refCtt closed"><span>Mukaka, M.M. 2012. Statistics corner: A guide to appropriate use of correlation coefficient in medical research. Malawi Med J. 24:69-71.</span></span></span>).</p>
+<h1 class="articleSectionTitle">Resultados e discussão<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>
+</h1>
+<p>Os fito-constituintes ou fitoquímicos são compostos químicos que desempenham importantes funções nas plantas. A triagem fitoquímica em materiais vegetais é geralmente o ponto de partida para o isolamento e purificação de compostos naturais com bioatividade (<span class="ref"><strong class="xref xrefblue">Omoregie &amp; Oikeh 2015</strong><span class="refCtt closed"><span>Omoregie, E.S. &amp; Oikeh, E.I. 2015. Comparative studies on the phytochemical composition, phenolic content and antioxidant activities of methanol leaf extracts of Spondias mombin and Polyathia longifolia. Jordan Journal of Biological Sciences 147: 1-5.</span></span></span>). A triagem fitoquímica preliminar revelou a presença de fenóis, taninos, flavonoides e esteroides para todos os extratos estudados (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>Tabela 2</a>). Entretanto, a presença de saponinas foi constatada apenas no EEF e EEC de <i>S. alata</i> e no EEF de <i>S. trachypus</i>. Já os alcaloides foram encontrados exclusivamente no EEF de <i>S. alata</i> e nenhuma das espécies apresentou triterpenoides. </p>
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+<strong><strong>Tablela 2</strong></strong><br> Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.<br>
+</div>
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+			</div>
+<p>Os metabólitos detectados nas espécies estudadas são consistentes com os metabólitos descritos na literatura para o gênero <i>Senna</i>, conhecido por apresentar flavonoides, alcaloides, taninos, esteroides e saponinas em sua composição (<span class="ref"><strong class="xref xrefblue">Onyegeme-Okerenta <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Onyegeme-Okerenta, B.M., Nwosu, T. &amp; Wegwu, M.O. 2017. Proximate and phytochemical composition of leaf extract of Senna alata (L) Roxb. Journal of Pharmacognosy and Phytochemistry 6: 320-326.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Ishaku <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Ishaku, G.A., Arabo, A.A., Bassey, E.E., Uwem, A.A.U.M. &amp; Godwin, E.U. 2016. Physicochemical characterization and antibacterial activity of Senna occidentalis Linn. Journal of Chemistryand Chemical Sciences 6: 9-18. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Sudi <i>et al</i>. 2011</strong><span class="refCtt closed"><span>Sudi, I.Y., Ksgbiya, D.M., Muluh, E.K. &amp; Clement, A. 2011. Nutritional and phytochemical screening of Senna obtusifolia indigenous to Mubi, Nigeria. Advances in Applied Science Research 2: 432-437.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bukar <i>et al.</i> 2009</strong><span class="refCtt closed"><span>Bukar, A., Mukhtar, M. &amp; HASSAN, A. 2009. Phytochemical screening and antibacterial activity of leaf extracts of Senna siamea (Lam) on Pseudomonas aeruginosa. Bayero Journal of Pure and Applied Sciences 1: 139-142. </span></span></span>). É possível perceber que na análise de prospecção química dos extratos houve uma variação de metabólitos secundários. Este fato pode estar atribuído a vários fatores, entre eles estão as diferentes condições ambientais, tais como clima, radiação solar, nutrição mineral, sazonalidade, ritmo circadiano, temperatura, disponibilidade hídrica, e também os tipos de solvente e a metodologia empregada no processo de extração, que podem interferir consideravelmente no conteúdo de praticamente todas as classes de metabólitos secundários (<span class="ref"><strong class="xref xrefblue">Gomes <i>et al</i>. 2016</strong><span class="refCtt closed"><span>Gomes, E.M.C., Pena, R.D.C.M. &amp; da Silva, S.S.S.M. 2016. Composição fitoquímica e ação fungicida de extratos brutos de Cinnamomum zeylanicum sobre Quambalaria eucalypti. Biota Amazônia. 6: 54-58.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Bezerra <i>et al.</i> 2013</strong><span class="refCtt closed"><span>Bezerra, A.S., Nörnberg, J.L., Lima, F.O., Rosa, M.B.D. &amp; Carvalho, L.M.D. 2013. Parâmetros climáticos e variação de compostos fenólicos em cevada. Ciência Rural 9: 1546-1552.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gobbo-Neto &amp; Lopes 2007</strong><span class="refCtt closed"><span>Gobbo-Neto, L. &amp; Lopes, N.P. 2007. Plantas medicinais: Fatores de influência no conteúdo de metabólitos secundários. Química Nova 30: 374-381.</span></span></span>).</p>
+<p>Os teores de fenóis totais apresentaram diferenças significativas entre os extratos etanólicos das diferentes partes e espécies vegetais estudadas (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). O conteúdo de fenóis totais para os EEF variou de 32,60 ± 0,53 a 184,8 ± 5,09 EAG/g, enquanto que para o EEC foram de 30,03± 1,00 a 191,3 ± 0,47 EAG/g. Os maiores níveis de fenóis totais foram detectados na espécie <i>S. trachypus</i>. Os dados da literatura sobre o conteúdo de compostos fenólicos obtidos a partir do extrato aquoso, etanólico e acetona da raiz de <i>S. alata</i>, apresentaram uma concentração de fenóis de 46,3, 78,21 e 21,42 mg EAG/g, respectivamente, e de flavonoides de 26,17, 39,29 e 9,65 mg de equivalente de quercetina por grama de extrato (EQ/g), respectivamente (<span class="ref"><strong class="xref xrefblue">Ita &amp; Ndukwe 2017</strong><span class="refCtt closed"><span>Ita, B.N., &amp; Ndukwe, G.I. Antioxidant activity of Senna alata root extracts. 2017. J Nat Prod Resour 3: 94-96. </span></span></span>). Já o extrato etanólico preparado a partir das folhas de <i>S. obtusifolia</i> por <span class="ref"><strong class="xref xrefblue">Ali <i>et al</i>. (2019</strong><span class="refCtt closed"><span>Ali, I., Yisa, J. &amp; Jacob, J.O. 2019. Corrosion inhibitory potential of ethanol extract of Senna obtusifolia on Mild Steel in 5M HCl. Journal of Chemical Society of Nigeria 44: 187-198. </span></span></span>), apresentou um teor de fenóis e de flavonoides de 14,39 mg/g e 2,85 mg/g, respectivamente, demonstrando possuir teor de compostos fenólicos inferior ao das mostras de <i>S. obtusifolia</i> encontradas no presente estudo. Além disso, o conteúdo de polifenóis encontrado no extrato etanólico e nas frações obtidas a partir das folhas de <i>S. occidentalis</i> por <span class="ref"><strong class="xref xrefblue">Yakubu <i>et al.</i> (2018</strong><span class="refCtt closed"><span>Yakubu, O.E., Otitoju, O., Imarenezor, E.P.K., Tatah, S.V. &amp; Habibu, B. 2018. Fractionation and determination of antioxidant activities, of the Leaves of Senna Occidentalis ethanol extract. Pharmacology, 6: 26-30.</span></span></span>) variou de 139 mg/mL a 206 mg/mL e de flavonoides de 104 a 142 mg/mL. Já para os extratos preparados a partir das folhas e casca do caule de <i>S. siamea</i> revelaram um teor de fenóis totais de 10,21 ± 0,25 g/g e 24,77 ± 0,15 g/g, respectivamente. Por outro lado, o teor de flavonoides foi de 0,08 ± 0,01 g/g para as folhagens, e de 0,04 ± 0,01 g/g para a casca do caule (<span class="ref"><strong class="xref xrefblue">Kwada &amp; Tella 2009</strong><span class="refCtt closed"><span>Kwada, A.D. &amp; Tella, I.O. 2009. Determination of infochemicals and the phytochemical screening of the foliage and stem-bark of Senna siamea (lam.) in Yola, Adamawa State. Journal of Medicinal Plants Research 3: 630-640.</span></span></span>). Para os extratos etanólicos das folhas e raízes de <i>S. trachypus</i> o teor de fenóis totais encontrado foi de 322,09 ± 2,83 EAG/g e de 1277,34 ± 79,54 EAG/g, respectivamente (<span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>).<i>Senna</i>.</p>
+<div>
+				<div class="row table" id="t3">
+<a name="t3"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Table 3.</strong></strong><br> Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).<br>
+</div>
+</div>
+			</div>
+<p>Os resultados da atividade antioxidante dos extratos de <i>Senna</i> spp. mostraram que os valores de CE<sub>50</sub> para o EEF variaram de 0,63 ± 0,01 a 8,20 ± 0,07 µg/mL, sendo o EEF de <i>S. trachypus</i> o que apresentou menor CE<sub>50</sub> com atividade antirradicalar superior ao da quercetina e, portanto, maior potencial antioxidante (<span class="ref"><strong class="xref xrefblue">Villano <i>et al</i>. 2007</strong><span class="refCtt closed"><span>Villano, D., Fernandez-Pachón, M.S., Moya, M.L., Troncoso, A.M. &amp; García-Parrilla, M.C. 2007. Radical scavenging ability of polyphenolic compounds towards DPPH free radical. Talanta, 71: 230-235. </span></span></span>). Já para o EEC os valores de CE<sub>50</sub> variaram de 0,83 ± 0,01 a 11,19 ± 0,15 µg/mL (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). Foi observado que o EEC de <i>S. siamea</i> apresentou capacidade antirradicalar próximo à quercetina. Semelhantes aos nossos resultados, estudos anteriores revelaram que as espécies de <i>S. alata, S. obtusifolia, S. occidentalis, S. siamea</i> e <i>S. trachypus</i>, apresentaram potencial antioxidante e que esta atividade está atribuída à presença de compostos fenólicos (<span class="ref"><strong class="xref xrefblue">Coelho <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Coelho, E.M.P., Barbosa, M.C., Mito, M.S., Mantovanelli, G.C., Oliveira, R.S., &amp; Ishii-Iwamoto, E.L. 2017. The activity of the antioxidant defense system of the weed species Senna obtusifolia L. and its resistance to allelochemical stress. Journal of Chemical Ecology 7: 725-738.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Ita &amp; Ndukwe 2017</strong><span class="refCtt closed"><span>Ita, B.N., &amp; Ndukwe, G.I. Antioxidant activity of Senna alata root extracts. 2017. J Nat Prod Resour 3: 94-96. </span></span></span>, <span class="ref"><strong class="xref xrefblue">Barnaby <i>et al.</i> 2016</strong><span class="refCtt closed"><span>Barnaby, A.G., Reid, R. &amp; Warren, D. 2016. Antioxidant activity, total phenolics and fatty acid profile of Delonix regia, Cassia fistula, Spathodea campanulata, Senna siamea and Tibouchina granulosa. J Anal Pharm Res 3: 00056.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Silva <i>et al.</i> 2014</strong><span class="refCtt closed"><span>Silva, G.A., Monteiro, J.A., Ferreira, E.B., Fernandes, M.I.B., Pessoa, C.; Sampaio, C.G. &amp; Silva, M.G.V. 2014. Total phenolic content, antioxidant and anticancer activities of four species of Senna Mill. From northeast Brazil. Int. J. Pharm. Pharm. Sci 6: 199-202.</span></span></span>). </p>
+<p>Os resultados obtidos na análise de inibição da enzima acetilcolinesterase foram comparados ao do alcaloide fisostigmina que foi o primeiro inibidor descoberto. Os experimentos de inibição da enzima acetilcolinesterase <i>in vitro</i> para as espécies de <i>Senna</i> produziram apenas resultados com potência moderada (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>Tabela 3</a>). Relatos confirmam a atividade antiacetilcolinesterásica de vários taninos isolados do fruto <i>Terminalia chebula</i> Retz.<i>,</i> (Combretaceae) que exibiram um efeito de inibição contra a enzima acetilcolinesterase <i>in vitro</i> (<span class="ref"><strong class="xref xrefblue">Kim <i>et al.</i> 2018</strong><span class="refCtt closed"><span>Kim, M.S., Lee, D.Y., Sung, S.H. &amp; Jeon, W.K. 2018. Anti-cholinesterase activities of hydrolysable tannins and polyhydroxytriterpenoid derivatives from Terminalia chebula Retz. fruit. Fruit Rec Nat Prod 12: 284-289.</span></span></span>). Outros compostos, como saponinas, alcaloides e compostos fenólicos, também são relatados na literatura como inibidores da enzima acetilcolinesterase (<span class="ref"><strong class="xref xrefblue">Paiva <i>et al</i>. 2021</strong><span class="refCtt closed"><span>Paiva, J.R., Queiroz, S.A.S., Pereira, R.D.C.A., Ribeiro, P.R.V., Alves, F.E.G., Silva, L.M.A., Zocolo, G.J., Brito, E.S., Alves, D.R., Morais, S.M., Tavares, J., Pinto, F.C.L., Andrade, G.M., Pessoa, O.D.L., &amp; Canuto, K.M. 2021. Chemical composition and anticholinesterase activity of cultivated bulbs from Hippeastrum elegans, a potential tropical source of bioactive alkaloids. Phytochemistry Letters 43: 27-34.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kozachok <i>et al</i>. 2020</strong><span class="refCtt closed"><span>Kozachok, S., Pecio, Ł., Orhan, I.E., Deniz, F.S.S., Marchyshyn, S., &amp; Oleszek, W. 2020. Reinvestigation of Herniaria glabra L. saponins and their biological activity. Phytochemistry 169: 112162.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Adedayo <i>et al</i>. 2015</strong><span class="refCtt closed"><span>Adedayo, B.C., Oboh, G., Oyeleye, S.I., Ejakpovi, I.I., Boligon, A.A., &amp; Athayde, M.L. 2015. Blanching alters the phenolic constituents and in vitro antioxidant and anticholinesterases properties of fireweed (Crassocephalum crepidioides). Journal of Taibah University Medical Sciences 10: 419-426.</span></span></span>). Estas classes de compostos foram detectadas na triagem fitoquímica, embora provavelmente as concentrações nos extratos eram muito baixas para dar resultados satisfatórios no ensaio. Os extratos foliares e do caule de <i>S. trachypus</i> apresentaram os valores mais satisfatórios de inibição da enzima acetilcolinesterase, indicando que o isolamento de metabólitos pode levar a potenciais agentes antiacetilcolinesterásicos. Na literatura, não foram encontrados estudos do potencial anticolinesterásico paras as espécies de <i>Senna</i> referenciadas, sendo este o primeiro relato de estudo de atividade de inibição para esta enzima. </p>
+<p>Para os extratos de <i>Senna</i> spp., foi observada forte correlação negativa entre os valores de fenóis totais e CE<sub>50</sub> (r = - 0,71), mostrando que quanto maior os teores de fenóis totais, menor a CE<sub>50</sub> e, consequentemente, maior o potencial antioxidante, uma vez que a CE<sub>50</sub> está inversamente relacionada à capacidade antioxidante de um composto (<span class="ref"><strong class="xref xrefblue">Villano <i>et al</i>. 2007</strong><span class="refCtt closed"><span>Villano, D., Fernandez-Pachón, M.S., Moya, M.L., Troncoso, A.M. &amp; García-Parrilla, M.C. 2007. Radical scavenging ability of polyphenolic compounds towards DPPH free radical. Talanta, 71: 230-235. </span></span></span>). Dentre os extratos analisados podemos observar na figura 1 o EEF de <i>S. trachypus.</i></p>
+<p>
+				<div class="row fig" id="">
+<a name=""></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf1.jpg" data-toggle="modal" data-target="#ModalFig"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf1.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Na correlação da atividade de inibição da enzima acetilcolinesterase, representada pelo CI<sub>50</sub> com teor de fenóis totais, observou-se uma correlação muito forte (r = -0,84) entre estas duas variáveis, evidenciando que ambas são inversamente proporcionais entre si, ou seja, à medida que o teor de fenóis totais aumenta o valor de CI<sub>50</sub> diminui, como pode ser observado para o EEF de <i>S. occidentalis</i> (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>Figura 2</a>). Isso demonstra que os compostos fenólicos podem ser determinantes nessa atividade, de modo que alguns estudos evidenciaram que flavonoides e outros compostos fenólicos possuem atividade anticolinesterásica (<span class="ref"><strong class="xref xrefblue">Amessis-Ouchemoukh <i>et al</i>. 2014</strong><span class="refCtt closed"><span>Amessis-Ouchemoukh, N., Madani, K., Falé, P.L., Serralheiro, M.L., Araújo, M.E.M. 2014. Antioxidant capacity and phenolic contents of some Mediterranean medicinal plants and their potential role in the inhibition of cyclooxygenase-1 and acetylcholinesterase activities. Industrial Crops and Products, 53: 6-15.</span></span></span>). </p>
+<p>
+				<div class="row fig" id="f2">
+<a name="f2"></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf2.jpg" data-toggle="modal" data-target="#ModalFigf2"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf2.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 2.</strong><br>Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Houve uma correlação moderada (r = 0,43) entre a CI<sub>50</sub> e a CE<sub>50</sub>. Analisando a <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>figura 3</a>, é possível perceber que o EEF e EEC de <i>S. alata</i> e EEF de <i>S. obtusifolia</i> se destacam no gráfico<i>,</i> o que sugere uma grande capacidade dos antioxidantes, como os compostos fenólicos, presentes nos extratos analisados, de atuarem não só através da inibição da acetilcolinesterase (AChEI) mas também por mecanismos de redução de radicais livres.</p>
+<p>
+				<div class="row fig" id="f3">
+<a name="f3"></a><div class="col-md-4 col-sm-4"><a href="2236-8906-hoehnea-49-e1112020-gf3.jpg" data-toggle="modal" data-target="#ModalFigf3"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf3.jpg"><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 3.</strong><br>Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</div>
+</div>
+			</p>
+<p>Os extratos etanólicos das folhas e caule de <i>S. alata, S. obtusifolia, S. occidentalis</i> e <i>S. siamea,</i> apresentaram efeito inibitório contra algumas cepas de <i>T. rubrum</i>. A maioria dos extratos foram eficazes em diferentes concentrações, com CIM que variaram de 0,07 mg/mL à 2,5 mg/mL e CFM de 0,15 a 5,0 mg/mL contra a grande maioria das cepas fúngicas testadas. Dentre os extratos testados, os de <i>S. trachypus</i> foram eficazes contra todas as cepas de <i>T. rubrum</i> com CIM que variaram de 0,31 a 0,62 mg/mL e o CFM de 0,62 a 1,25 mg/mL, para ambos os extratos (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>Tabela 4</a>). A presença de compostos fitoquímicos tem sido associada às atividades antimicrobianas da maioria dos materiais vegetais. Algumas classes de metabólitos foram identificadas nesse estudo e podem ser associadas à atividade antimicrobiana (<span class="ref"><strong class="xref xrefblue">Santos <i>et al.</i> 2018</strong><span class="refCtt closed"><span>Santos, T.C.D., Gomes, T.M., Pinto, B.A.S., Camara, A.L. &amp; Paes, A.M.D.A. 2018. Naturally occurring acetylcholinesterase inhibitors and their potential use for Alzheimer's disease therapy. Frontiers in Pharmacology 9: 1192.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>). </p>
+<div>
+				<div class="row table" id="t4">
+<a name="t4"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 4. </strong></strong><br> Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.<br>
+</div>
+</div>
+			</div>
+<p>Estudos anteriores realizados com o extrato etanólico da casca do caule de <i>S. alata</i> contra fungos dermatofíticos, entre eles espécies de <i>Trychophyton,</i> revelou um CIM de 5,0 mg/mL para todos os dermatófitos testados (<span class="ref"><strong class="xref xrefblue">Sule <i>et al.</i> 2011</strong><span class="refCtt closed"><span>Sule, W.F., Okonko, I.O., Omo-Ogun, S., Nwanze, J.C., Ojezele, M.O., Ojezele, O.J., Alli, J.A., Soyemi, E.T. &amp; Olaonipekun, T.O. 2011. Phytochemical properties and in-vitro antifungal activity of Senna alata Linn. crude stem bark extract. Journal of Medicinal Plants Research, 5: 176-183.</span></span></span>). A capacidade antifúngica de extratos de diferentes polaridades preparados a partir das folhas de <i>S. obtusifolia</i> apresentaram um CIM que variou de 500 a 2000 µg/mL contra diferentes espécies de fungos filamentosos (<span class="ref"><strong class="xref xrefblue">Doughari <i>et al.</i> 2008</strong><span class="refCtt closed"><span>Doughari, J.H., El-mahmood, A.M. &amp; Tyoyina, I. 2008. Antimicrobial activity of leaf extracts of Senna obtusifolia (L). African Journal of Pharmacy and Pharmacology 2: 7-13.</span></span></span>). Os resultados obtidos de extratos foliares de polaridades diferentes de <i>S. occidentalis</i> revelaram que o extrato metanólico mostrou maior atividade antifúngica entre os demais extratos testados, em uma concentração inibitória mínima de 25 mg/mL (<span class="ref"><strong class="xref xrefblue">Odeja <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Odeja, O., Obi, G., Ogwuche, C.E., Elemike, E.E. &amp; Oderinlo, Y. 2015. Phytochemical Screening, Antioxidant and Antimicrobial activities of Senna occidentalis (L.) leaves Extract. Clinical Phytoscience 1: 1-6.</span></span></span>). Testes utilizando extratos preparados com solventes de diferentes polaridades a partir das folhas de <i>S. siamea</i> apresentaram CIM que variaram de 0,032 a 0,128 mg/mL contra o fungo <i>Cryptococcus gattii</i> (<span class="ref"><strong class="xref xrefblue">Nnadi <i>et al.</i> 2019</strong><span class="refCtt closed"><span>Nnadi, N.E., Anukam, N.C., Ayika, P.D., Rotdung, K., Gokum, S.S., Ayanbimpe, G.M., Nvau, J. &amp; Enweani, I. 2019. The in Vitro antifungal activity of some Nigeria medicinal plants against Cryptococcus gattii. IOSR Journal of Pharmacy 9: 16-24. </span></span></span>). Na literatura, não foram encontrados estudos do potencial antifúngico para a espécie de <i>S. trachypus</i>, sendo este o primeiro registro de atividade antifúngica para a referida espécie. </p>
+<p>Pesquisas têm revelado que o potencial antifúngico de extratos vegetais está intimamente relacionado, entre outros fatores, com as suas variações quantitativas de compostos fenólicos, dentre eles os flavonoides. Nosso estudo confirmou que as espécies estudadas possuem propriedades antifúngicas, e que seus efeitos sobre os dermatófitos fundamentam-se em seus teores de compostos fenólicos encontrados, e os demais outros metabólitos secundários aqui não estudados. Os efeitos antifúngicos atribuídos aos compostos fenólicos podem resultar na ruptura da membrana celular, ou ainda, inibir a divisão celular e o desenvolvimento das hifas por meio de genes específicos, além de interferir nas vias metabólicas e/ou induzir a apoptose por perturbar a homeostase redox (<span class="ref"><strong class="xref xrefblue">Lagrouh <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Lagrouh, F., Dakka, N. &amp; Bakri, Y. 2017.The antifungal activity of Moroccan plants and the mechanism of action of secondary metabolites from plants. Journal de Mycologie Medicale 27: 303-311.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Mohamed <i>et al.</i> 2017</strong><span class="refCtt closed"><span>Mohamed, M.S., Saleh, A.M., Abdel-Farid, I.B. &amp; El-Naggar, S.A. 2017. Growth, hydrolases and ultrastructure of Fusarium oxysporum as affected by phenolic rich extracts from several xerophytic plants. Pesticide Biochemistry and Physiology 141: 57-64. </span></span></span>).</p>
+<p>Foram detectados, nos EEF e EEC das espécies de <i>Senna</i>, a presença de metabólitos secundários, alto teor de fenóis totais e capacidade antioxidante para todas as espécies, em especial <i>S. trachypus</i>. Para a atividade anticolinesterase apenas a espécie de <i>S. trachypus</i> manifestou uma melhor ação inibitória. Nas condições experimentais utilizadas, evidenciou-se atividade antifúngica das espécies frente a maioria dos dermatófitos testados, em especial os extratos de <i>S. trachypus</i>. Foi observada também correlação forte, muito forte e moderada entre as variáveis fenóis totais e atividade antioxidante, fenóis totais e antiacetilcolinesterase e atividade antioxidante e antiacetilcolinesterase, respectivamente<i>.</i> Os resultados apontam que <i>S. trachypus</i>, espécie endêmica da Caatinga, é a mais promissora entre todas as plantas estudadas, representando uma fonte potencial para a obtenção de compostos químicos úteis para estudos clínicos e farmacológicos, visando o desenvolvimento de novos agentes farmacológicos naturais. </p>
+</div>
+<div class="articleSection" data-anchor="Agradecimentos">
+<h1 class="articleSectionTitle">Agradecimentos</h1>
+<p>Os autores agradecem a Universidade Estadual do Ceará (UECE) e a Universidade Estadual Vale do Acaraú (UVA) pelo apoio técnico, e a Fundação Cearense de Apoio ao Desenvolvimento Científico e Tecnológico (FUNCAP) pelo apoio financeiro concedido (processos PBI3-0139-00252.01.00/18; BP4-0172-00170.01.00/20). </p>
+</div>
+<div class="articleSection" data-anchor="Literatura citada">
+<h1 class="articleSectionTitle">Literatura citada</h1>
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+</ul></div>
+</div>
+<div class="articleSection" data-anchor="Datas de Publicação ">
+<h1 class="articleSectionTitle">Datas de Publicação </h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Publicação nesta coleção</strong><br>21 Fev 2022</li>
+<li>
+<strong>Data do Fascículo</strong><br>2022</li>
+</ul></div></div>
+</div>
+<div class="articleSection" data-anchor="Histórico">
+<h1 class="articleSectionTitle">Histórico</h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Recebido</strong><br>14 Out 2020</li>
+<li>
+<strong>Aceito</strong><br>03 Dez 2021</li>
+</ul></div></div>
+</div>
+<section class="documentLicense"><div class="container-license"><div class="row">
+<div class="col-sm-3 col-md-2"><a href="https://creativecommons.org/licenses/by/4.0/" target="_blank" title=""><img src="https://licensebuttons.net/l/by/4.0//88x31.png" alt="Creative Common - by 4.0 "></a></div>
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+<div class="tutors">
+<strong> Andréa Maria Neves </strong><strong>4</strong><br><div> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-7388-1844" class="btnContribLinks orcid">http://orcid.org/0000-0002-7388-1844</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Selene Maia de Morais </strong><br><div> Universidade Estadual do Ceará, Centro de Ciências e Tecnologia, Programa de Pós-graduação em Biotecnologia, Avenida Doutor Silas Muguba, 1700, Itaperi, 60740-000 Fortaleza, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2766-3790" class="btnContribLinks orcid">http://orcid.org/0000-0002-2766-3790</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Hélcio Silva dos Santos </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Exatas e Tecnologia, Curso de Química, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0001-5527-164X" class="btnContribLinks orcid">http://orcid.org/0000-0001-5527-164X</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Marcílio Matos Ferreira </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0003-2503-9772" class="btnContribLinks orcid">http://orcid.org/0000-0003-2503-9772</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Ricardo Carneiro Vera Cruz </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2035-0425" class="btnContribLinks orcid">http://orcid.org/0000-0002-2035-0425</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Elnatan Bezerra de Souza </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-5222-4378" class="btnContribLinks orcid">http://orcid.org/0000-0002-5222-4378</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Lúcia Betânia da Silva Andrade </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-4384-5738" class="btnContribLinks orcid">http://orcid.org/0000-0002-4384-5738</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Raquel Oliveira dos Santos Fontenelle </strong><br><div> Universidade Estadual Vale do Acaraú, Centro de Ciências Agrárias e Biológicas, Curso de Ciências Biológicas, Avenida da Universidade, 850, Betânia, 62040-370 Sobral, CE, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-8865-5954" class="btnContribLinks orcid">http://orcid.org/0000-0002-8865-5954</a></li></ul>
+<div class="clearfix"></div>
+</div>
+</div>
+<div class="info">
+					<h3><sup>4</sup></h3> Autor para correspondência: <a href="mailto:andreamarianeves@gmail.com">andreamarianeves@gmail.com</a>
+				</div>
+<div class="info">
+<h3>Editora Associada:</h3>
+<div> Catarina Carvalho Nievola</div>
+</div>
+<div class="info">
+<h3>Contribuição dos autores</h3>
+<div>
+<b>Andréa Maria Neves:</b> Contribuição substancial em todas as etapas da pesquisa e para a confecção do manuscrito. <b>Selene Maia de Morais:</b> Contribuição na realização do teste de acetilcolinesterase; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Hélcio Silva dos Santos:</b> Contribuição na preparação dos extratos; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Marcílio Matos Ferreira:</b> Contribuição para a coleta das espécies e preparação dos extratos. <b>Ricardo Carneiro Vera Cruz:</b> Contribuição na realização dos testes fitoquímicos e quantificação de fenóis totais. <b>Elnatan Bezerra de Souza:</b> Contribuição na coleta e identificação das espécies; Contribuição na revisão crítica do manuscrito, agregando conteúdo intelectual. <b>Lúcia Betânia da Silva Andrade:</b> Contribuição na realização da atividade antioxidante, para a interpretação dos dados, e para revisão crítica, agregando conteúdo intelectual. <b>Raquel Oliveira dos Santos Fontenelle:</b> Contribuição nos testes antifúngicos e para revisão crítica, agregando conteúdo intelectual. </div>
+</div>
+<div class="info">
+<h3>Conflitos de interesse</h3>
+<div> Os autores declaram não haver conflitos de interesse a informar.</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Figuras | Tabelas</h4>
+</div>
+<div class="modal-body">
+<ul class="nav nav-tabs md-tabs" role="tablist">
+<li role="presentation" class="col-md-4 col-sm-4 active"><a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">Figuras
+                    (3)
+                </a></li>
+<li role="presentation" class="col-md-4 col-sm-4 "><a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">Tabelas
+                    (4)
+                </a></li>
+</ul>
+<div class="clearfix"></div>
+<div class="tab-content">
+<div role="tabpanel" class="tab-pane active" id="figures">
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFig"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf1.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 1.</strong><br>Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf2"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf2.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 2.</strong><br>Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf3"><div class="thumbImg">
+<img src="2236-8906-hoehnea-49-e1112020-gf3.jpg">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 3.</strong><br>Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.</div>
+</div>
+</div>
+<div role="tabpanel" class="tab-pane " id="tables">
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 1.</strong></strong><br> Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tablela 2</strong></strong><br> Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Table 3.</strong></strong><br> Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 4. </strong></strong><br> Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.</div>
+</div>
+</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFig" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf1.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 1.   Correlação entre o teor de fenóis totais e CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf1.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf1.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1"><span class="sci-ico-fileFigure"></span>Figure 1</a>. Correlation between total phenol content and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf2.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 2.   Correlação entre o teor de fenóis totais e CI50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf2.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf2.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>Figure 2</a>. Correlation between total phenol content and IC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1112020-gf3.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 3.   Correlação entre CI50 e a CE50 de espécies de <i>Senna</i> Mill. (Fabaceae). Símbolos cheios: folhas. Símbolos vazados: caule.<br>
+</h4>
+</div>
+<div class="modal-body">
+<a href="2236-8906-hoehnea-49-e1112020-gf3.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1112020-gf3.jpg"></a><small><a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>Figure 3</a>. Correlation between IC50 and EC50 of Senna Mill species. (Fabaceae). Symbols filled: leaves. Hollow symbols: stem.</small>
+</div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 1.</strong>    Identificação das espécies de <i>Senna</i> Mill. (Fabaceae) coletadas em diferentes locais da região noroeste do Estado do Ceará. <sup>*</sup>Exótica, <sup>**</sup>Endêmica do Brasil. Fonte: Herbário Francisco José de Abreu Matos (HUVA).<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col>
+<col>
+<col>
+</colgroup>
+<thead><tr>
+<th align="left">Espécies</th>
+<th align="left">Nome popular</th>
+<th align="center">Local de coleta</th>
+<th align="center">No. HUVA</th>
+</tr></thead>
+<tbody>
+<tr>
+<td align="left">
+<i>S. alata</i> (L.) Roxb.</td>
+<td align="left">fedegoso-gigante</td>
+<td align="center">Sobral</td>
+<td align="center">21547</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (L.) H.S.Irwin &amp; Barneby</td>
+<td align="left">fedegoso-brando</td>
+<td align="center">Graça</td>
+<td align="center">21775</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (L.) Link</td>
+<td align="left">café-negro</td>
+<td align="center">Graça</td>
+<td align="center">21774</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Lam.) H.S.Irwin &amp; Barneby<sup>*</sup>
+</td>
+<td align="left">cássia-de-sião</td>
+<td align="center">Sobral</td>
+<td align="center">21578</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Benth.) H.S.Irwin &amp; Barneby<sup>**</sup>
+</td>
+<td align="left">pau-de-besouro</td>
+<td align="center">Graça</td>
+<td align="center">21776</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>Table 1</a>Identification of <i>Senna Senna</i> Mill. (Fabaceae) species collected in different locations in northwestern Ceará State. <sup>*</sup> Exotic, <sup>**</sup> Endemic to Brazil. Source: Herbário Francisco José de Abreu Matos (HUVA).</div></li></ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tablela 2</strong>    Triagem fitoquímica do EEF e do EEC de espécies de <i>Senna</i> Mill. (Fabaceae)<i>.</i> Presente: + Ausente: - EEF: Extrato etanólico da folha. EEC: Extrato etanólico do caule.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup><col span="11"></colgroup>
+<thead>
+<tr><th align="center" colspan="11">Espécies </th></tr>
+<tr>
+<th align="left">Metabólitos</th>
+<th align="left" colspan="2"><i>S. alata</i></th>
+<th align="left" colspan="2"><i>S. obtusifolia</i></th>
+<th align="left" colspan="2"><i>S. occidentalis</i></th>
+<th align="left" colspan="2"><i>S. siamea</i></th>
+<th align="left" colspan="2"><i>S. trachypus</i></th>
+</tr>
+<tr>
+<th align="left">Extratos</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+<th align="left">EEF</th>
+<th align="left">EEC</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">Flavonoides</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Fenóis</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Saponinas</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">+</td>
+<td align="left">-</td>
+</tr>
+<tr>
+<td align="left">Taninos</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Esteroides</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+<td align="left">+</td>
+</tr>
+<tr>
+<td align="left">Alcaloides</td>
+<td align="left">+</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+</tr>
+<tr>
+<td align="left">Triterpenoides</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+<td align="left">-</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>Table 2</a>. Phytochemical screening of EEF and EEC of <i>Senna</i> Mill. (Fabaceae) species. Present: + Absent: - EEF: Ethanol extract of the leaf. EEC: Ethanol extract from the stem.</div></li></ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Table 3.</strong>    Teor de fenóis totais, atividade antioxidante e inibição da enzima acetilcolinesterase de espécies de Senna Mill. (Fabaceae).<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col span="2">
+<col span="2">
+<col span="2">
+</colgroup>
+<thead>
+<tr>
+<th align="left" rowspan="2">Espécies</th>
+<th align="center" colspan="2">Fenois<sup>1</sup> mg EAG.g<sup>-1</sup> de extrato </th>
+<th align="center" colspan="2">DPPH<sup>2</sup> CE<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+<th align="center" colspan="2"> AChEI<sup>3</sup> CI<sub>50</sub> (μg.mL<sup>-1</sup>)</th>
+</tr>
+<tr>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+<th align="center">Média</th>
+<th align="center">Despad</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">
+<i>S. alata</i> (Folhas)</td>
+<td align="center">53,76 <sup>f</sup>
+</td>
+<td align="center">± 0,74</td>
+<td align="center">3,70 <sup>e</sup>
+</td>
+<td align="center">± 0,04</td>
+<td align="center">49,42 <sup>f</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. alata</i> (Caule)</td>
+<td align="center">43,44 <sup>g</sup>
+</td>
+<td align="center">± 0,21</td>
+<td align="center">5,41 <sup>c</sup>
+</td>
+<td align="center">± 0,06</td>
+<td align="center">53,25 <sup>d</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (Folhas)</td>
+<td align="center">76,32 <sup>e</sup>
+</td>
+<td align="center">± 0,41</td>
+<td align="center">4,24 <sup>d</sup>
+</td>
+<td align="center">± 0,06</td>
+<td align="center">50,37 <sup>e</sup>
+</td>
+<td align="center">± 0,32</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. obtusifolia</i> (Caule)</td>
+<td align="center">86,20 <sup>d</sup>
+</td>
+<td align="center">± 0,99</td>
+<td align="center">3,00 <sup>g</sup>
+</td>
+<td align="center">± 0,05</td>
+<td align="center">56,90 <sup>c</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (Folhas)</td>
+<td align="center">32,60 <sup>h</sup>
+</td>
+<td align="center">± 0,53</td>
+<td align="center">8,20 <sup>b</sup>
+</td>
+<td align="center">± 0,07</td>
+<td align="center">58,76 <sup>b</sup>
+</td>
+<td align="center">± 0,78</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. occidentalis</i> (Caule)</td>
+<td align="center">30,03 <sup>h</sup>
+</td>
+<td align="center">± 1,00</td>
+<td align="center">11,19 <sup>a</sup>
+</td>
+<td align="center">± 0,15</td>
+<td align="center">57,26 <sup>c</sup>
+</td>
+<td align="center">± 0,02</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Folhas)</td>
+<td align="center">51,73 <sup>f</sup>
+</td>
+<td align="center">± 0,85</td>
+<td align="center">3,34 <sup>f</sup>
+</td>
+<td align="center">± 0,05</td>
+<td align="center">59,77 <sup>a</sup>
+</td>
+<td align="center">± 0,26</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. siamea</i> (Caule)</td>
+<td align="center">111,7 <sup>c</sup>
+</td>
+<td align="center">± 3,43</td>
+<td align="center">0,83 <sup>i</sup>
+</td>
+<td align="center">± 0,01</td>
+<td align="center">59,52 <sup>ab</sup>
+</td>
+<td align="center">± 0,15</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Folhas)</td>
+<td align="center">184,80 <sup>b</sup>
+</td>
+<td align="center">± 5,09</td>
+<td align="center">0,63 <sup>k</sup>
+</td>
+<td align="center">± 0,01</td>
+<td align="center">32,40 <sup>g</sup>
+</td>
+<td align="center">± 0,12</td>
+</tr>
+<tr>
+<td align="left">
+<i>S. trachypus</i> (Caule)</td>
+<td align="center">191,3 <sup>a</sup>
+</td>
+<td align="center">± 0,47</td>
+<td align="center">2,52 <sup>h</sup>
+</td>
+<td align="center">± 0,03</td>
+<td align="center">31,44 <sup>h</sup>
+</td>
+<td align="center">± 0,14</td>
+</tr>
+<tr>
+<td align="left">Quercetina</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">1,03 <sup>i</sup>
+</td>
+<td align="center">± 0,00</td>
+<td align="center">-</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">Fisiostigmina</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">1,15 <sup>i</sup>
+</td>
+<td align="center">± 0,00</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote">
+<li><div>Total phenol content, antioxidant activity and acetylcholinesterase enzyme inhibition of <i>Senna</i> Mill. (Fabaceae) species. </div></li>
+<li><div>Todas as análises foram realizadas em triplicada e os resultados foram expressos como média ± desvio padrão. As diferenças entre os valores foram examinadas usando análise de variância (ANOVA) e os resultados foram comparados usando o teste de Tukey com 95% nível de confiança. Letras diferentes denotam diferença estatística entre os valores de cada coluna (p &lt; 0,05). <sup>1</sup>Miligrama equivalente ao Ácido Gálico por grama de extrato; <sup>2</sup>Concentração efetiva para inibir 50% do radical livre DPPH (2,2 -difenil-1-picril-hidrazil); <sup>3</sup>Concentração inibitória capaz de inibir 50% da acetilcolinesterase. (-) Testes não realizados.</div></li>
+<li><div>All analyzes were performed in triplicate and the results were expressed as mean ± standard deviation. The differences between the values ​​were examined using analysis of variance (ANOVA) and the results were compared using the Tukey test at 95% confidence level. Different letters denote statistical difference between the values ​​of each column (p &lt;0.05). <sup>1</sup> milligram Equivalent to Gallic Acid per gram of extract; <sup>2</sup>Effective concentration to inhibit 50% of the free radical DPPH (2,2 - diphenyl - 1 - picryl - hydrazil); <sup>3</sup>Inhibitory concentration capable of inhibiting 50% of acetylcholinesterase. (-) Tests not performed.</div></li>
+</ul></div></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 4. </strong>    Concentração Inibitória Mínima (CIM) e Concentração Fungicida Mínima (CFM) de extratos etanólicos (EEs) de espécies de <i>Senna</i> Mill. (Fabaceae) frente às espécies de <i>Trichophyton rubrum</i>. LABIMIC: Laboratório de Microbiologia; EEF: Extrato etanólico da folha; EEC: Extrato etanólico do caule; NI: Não inibiu.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<colgroup>
+<col>
+<col>
+<col span="2">
+<col span="2">
+<col span="2">
+<col span="2">
+</colgroup>
+<thead>
+<tr>
+<th align="left" rowspan="4">Espécies</th>
+<th align="center" rowspan="4">Extrato</th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+<th align="center" colspan="2"><i>T. rubrum</i></th>
+</tr>
+<tr>
+<th align="center" colspan="2">LABIMIC 5906 </th>
+<th align="center" colspan="2">LABIMIC 6213 </th>
+<th align="center" colspan="2">LABIMIC 6205 </th>
+<th align="center" colspan="2">LABIMIC 6753 </th>
+</tr>
+<tr>
+<th align="center">CIM</th>
+<th align="center">CFM </th>
+<th align="center">CIM </th>
+<th align="center">CFM</th>
+<th align="center">CIM</th>
+<th align="center">CFM</th>
+<th align="center">CIM</th>
+<th align="center">CFM</th>
+</tr>
+<tr>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+<th align="center" colspan="2">(mg/mL) </th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left" rowspan="2"><i>S. alata</i></td>
+<td align="center">EEF</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. obtusifolia</i></td>
+<td align="center">EEF</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. occidentalis</i></td>
+<td align="center">EEF</td>
+<td align="center">0,07</td>
+<td align="center">0,15</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. siamea</i></td>
+<td align="center">EEF</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">1,25</td>
+<td align="center">2,5</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+<td align="center">NI</td>
+<td align="center">-</td>
+<td align="center">2,5</td>
+<td align="center">5,0</td>
+</tr>
+<tr>
+<td align="left" rowspan="2"><i>S. trachypus</i></td>
+<td align="center">EEF</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="center">EEC</td>
+<td align="center">0,62</td>
+<td align="center">1,25</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+<td align="center">0,31</td>
+<td align="center">0,62</td>
+</tr>
+<tr>
+<td align="left">Cetoconazol</td>
+<td align="center"> </td>
+<td align="center">2,0</td>
+<td align="center"> </td>
+<td align="center">1,0</td>
+<td align="center"> </td>
+<td align="center">1,0</td>
+<td align="center"> </td>
+<td align="center">0,5</td>
+<td align="center"> </td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"><div class="ref-list"><ul class="refList footnote"><li><div>
+<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>Table 4</a>.  Minimum Inhibitory Concentration (MIC) and Minimum Fungicidal Concentration (MFC) of ethanolic extracts (EEs) from <i>Senna</i> Mill. LABIMIC: Microbiology Laboratory; EEF: Ethanol extract of the leaf; EEC: Ethanol extract from the stem; NI: It didn't inhibit. (Fabaceae) species compared to <i>Trichophyton rubrum</i> species.</div></li></ul></div></div>
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+<h1 class="article-title">
+<span class="sci-ico-openAccess showTooltip" data-toggle="tooltip" data-original-title="by 4.0 "></span>Florestas secundárias do Parque Estadual da Cantareira, São Paulo, SP, Brasil: Variações florísticas e estruturais<span class="ref footnote"><sup class="xref">1</sup><span class="refCtt closed"><span class="refCttPadding"><strong class="fn-title">1</strong>Parte da Dissertação de Mestrado do primeiro Autor</span></span></span><a id="shorten" href="#" class="short-link"><span class="sci-ico-link"></span></a>
+</h1>
+<h2 class="article-title">Secondary forests of the Parque Estadual da Cantareira, São Paulo State, SP, Brasil: Floristic and structural variations</h2>
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+<span class="dropdown"><a id="contribGroupTutor1" class="dropdown-toggle" data-toggle="dropdown"><span> Rafaela Dias Valeck da Silva </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor1">
+<strong></strong>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil<div class="corresp">4 Autora para correspondência: <a href="mailto:rafaela_valeck@hotmail.com">rafaela_valeck@hotmail.com</a>
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+<strong></strong>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil<a href="http://orcid.org/0000-0002-2626-5280" class="btnContribLinks orcid">http://orcid.org/0000-0002-2626-5280</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor3" class="dropdown-toggle" data-toggle="dropdown"><span> Frederico Alexandre Roccia Dal Pozzo Arzolla </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor3">
+<strong></strong>Instituto Florestal, Rua do Horto, 931, 02377-000 São Paulo, SP, Brasil<a href="http://orcid.org/0000-0003-3111-6877" class="btnContribLinks orcid">http://orcid.org/0000-0003-3111-6877</a>
+</ul></span><a href="" class="outlineFadeLink" data-toggle="modal" data-target="#ModalTutors">Sobre os autores</a>
+</div>
+<div class="row">
+<ul class="col-md-2 hidden-sm articleMenu"></ul>
+<article id="articleText" class="col-md-10 col-md-offset-2 col-sm-12 col-sm-offset-0"><div class="articleSection" data-anchor="RESUMO">
+<h1 class="articleSectionTitle">RESUMO</h1>
+<p>O Parque Estadual da Cantareira, no bioma da Mata Atlântica, foi criado a partir da desapropriação de fazendas de café para proteção de mananciais para a cidade de São Paulo em 1877. Desde então, poucas atividades humanas ocorreram em seu interior. Aqui, comparamos a composição e o estágio sucessional de diferentes fragmentos de floresta próximos (&lt;0,5 km um do outro). Foram levantados 0,6 ha, divididos em três áreas de 0,2 ha cada, com árvores atingindo PAP ≥ 15 cm, sendo amostradas, identificadas e medidos o diâmetro e a altura. O estágio sucessional das espécies foi determinado e um perfil de cada área foi desenhado em escala. Um total de 1.020 indivíduos pertencentes a 45 famílias e 115 espécies foi amostrado. Os fragmentos variaram em número de indivíduos (300-399 indivíduos), famílias (N = 26-32) e espécies (N = 54-68), altura e estágios sucessionais, indicando alta heterogeneidade dentro de uma floresta contínua, desde os estágios sucessionais maduros até os iniciais. Essas descobertas têm implicações para o manejo da conservação e os serviços ecossistêmicos fornecidos por eles.</p>
+<p><strong>Palavras-chave:</strong><br>Fitossociologia; Mata Atlântica; sucessão</p>
+</div>
+<div class="articleSection" data-anchor="ABSTRACT">
+<h1 class="articleSectionTitle">ABSTRACT</h1>
+<p>The Parque Estadual da Cantareira, in the Atlantic Forest biome, was created from the expropriation of coffee farms for the protection of water sources for São Paulo city in 1877. Since then, few human activities have taken place in its interior. Here, we compare the composition and the successional stages of different fragments of near forests (&lt;0.5 km of each other); 0.6 ha were raised, divided in three areas of 0.2 ha each, with trees reaching PAP ≥ 15 cm, being sampled, identified and measured for diameter and height. The succession stage of the species was determined and a profile of each area was drawn in scale. A total of 1,020 individuals of 45 families and 115 species was sampled. The fragments varies in number of in individuals (300-399 individuals), families (N = 26-32) and species (N = 54-68), height and successional stages, indicating high heterogeneity within a continuous forest, from the mature successional stages to the first ones. These discoveries have implications for conservation management and the ecosystem service they provide.</p>
+<p><strong>Keywords:</strong><br>Atlantic Rainforest; Phytosociology; succession</p>
+</div>
+<div class="articleSection" data-anchor="Text">
+<h1 class="articleSectionTitle">Introdução</h1>
+<p>A Mata Atlântica ocupa aproximadamente 15% do território brasileiro sendo considerada mundialmente o 5º bioma mais ameaçado (<span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>). Estende-se desde o Piauí até o Estado do Rio Grande do Sul, englobando assim 17 Estados brasileiros (<span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>). A ampla variação de temperatura, relevo e solo ao longo da Mata Atlântica, fazem desta uma das florestas de maior biodiversidade do mundo (<span class="ref"><strong class="xref xrefblue">Leitão-Filho 1987</strong><span class="refCtt closed"><span>Leitão-Filho, H.F. 1987. Considerações sobre a florística de florestas tropicais e sub-tropicais do Brasil. IPEF 45: 41-46.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Lino &amp; Amaral 2018</strong><span class="refCtt closed"><span>Lino, C.F. &amp; Amaral, M.M. 2018. Mata Atlântica e Sociobiodiversidade: Desafios e caminhos para a sustentabilidade. CN-RBMA Conselho Nacional da Reserva da Biosfera da Mata Atlântica. São Paulo: IA- RBMA.</span></span></span>). Pelo alto número de espécies endêmicas e forte pressão antrópica, o Bioma Mata Atlântica, juntamente com o Cerrado, é considerado um dos hostspots do planeta (<span class="ref"><strong class="xref xrefblue">Myers <i>et al</i>. 2000</strong><span class="refCtt closed"><span>Myers, N., Mittermeier, R.A., Mittermeier, C.G., Fonseca, G.A.B. 2000. Kent, J. Biodiversity hotspots for conservation priorities. Nature 403: 853-845.</span></span></span>)</p>
+<p>A Mata Atlântica é composta pelas seguintes formações vegetais: Floresta Ombrófila Densa, Aberta e Mista (conhecida como Floresta de Araucárias); Floresta Estacional Semidecidual e Decidual; Campos de Altitude; Manguezais, Restingas, Campos Salinos e Áreas Aluviais; Áreas de Tensão Ecológica; Refúgios Vegetacionais (<span class="ref"><strong class="xref xrefblue">IBGE 2019</strong><span class="refCtt closed"><span>IBGE. Fundação Instituto Brasileiro de Geografia e Estatística. Disponível em http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html (acesso em 16-XI-2019).</span><br><a href="http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html" target="_blank">http://7a12.ibge.gov.br/vamos-conhecer-o...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>).</p>
+<p>As Florestas Ombrófilas Densas se subdividem em 5 grupos principais: Floresta Ombrófila Densa de Terras Baixas, presente até 50 metros de altitude; Floresta Ombrófila Densa Submontana, 50 a 500 metros; Floresta Ombrófila Densa Montana, 500 a 1500 metros e a Floresta Ombrófila Densa Altomontana, acima de 1500 metros, e a Floresta Ombrófila Densa Aluvial, presente em qualquer das formações anteriores, ao longo dos cursos d’água (<span class="ref"><strong class="xref xrefblue">IBGE 2012</strong><span class="refCtt closed"><span>IBGE. 2012. Fundação Instituto Brasileiro de geografia e Estatística. Manual técnico da vegetação brasileira. 2ed, Rio de Janeiro.</span></span></span>).</p>
+<p>No Estado de São Paulo, a diminuição drástica da cobertura florestal deveu-se a fatores antrópicos, principalmente o estabelecimento de culturas, inicialmente a do café e o adensamento populacional nos núcleos urbanos (<span class="ref"><strong class="xref xrefblue">Rocha &amp; Costa 1998</strong><span class="refCtt closed"><span>Rocha, A.A. &amp; Costa, J.P.O. 1998. A Reserva da Biosfera da Mata Atlântica e sua aplicação no Estado de São Paulo: apresentação Covas, M.; prefácio Feldmann, F. J. - São Paulo: Terra Virgem, Secretaria do Meio Ambiente do Estado de São Paulo.</span></span></span>, RBMA 2019).</p>
+<p>Apesar da destruição da floresta ao longo da história de São Paulo, o Estado ainda preserva a maior área contínua da Mata Atlântica no Brasil, nas encostas da Serra do Mar (<span class="ref"><strong class="xref xrefblue">Leite 2007</strong><span class="refCtt closed"><span>Leite, M. 2007. Nos caminhos da Biodiversidade Paulista / Nas Costas do Brasil. Os litorais paulistas. São Paulo: Secretaria do Meio Ambiente: Instituto Amigos da Reserva da Biosfera da Mata Atlântica: Imprensa oficial do Estado de São Paulo.</span></span></span>). Alguns trabalhos mais recentes relatam o aumento da cobertura florestal, representada por florestas secundárias em diferentes estágios de regeneração (<span class="ref"><strong class="xref xrefblue">Farinaci &amp; Batistella 2012</strong><span class="refCtt closed"><span>Farinaci, J.S. &amp; Batistella, E.M. 2012. Variação na cobertura vegetal nativa em São Paulo: Um panorama do conhecimento atual. Revista Árvore 36(4): 695-705, 2012.</span></span></span>).</p>
+<p>O que resta da Mata Atlântica está inserido em 1.324 Unidades de Conservação (UCs). As Unidades de Conservação possuem uma classificação própria, pois a diversidade do ambiente resulta em objetivos e manejos distintos.</p>
+<p>A sucessão é o processo natural de desenvolvimento da comunidade vegetal que possibilita o estabelecimento de plantas em uma área desprovida de vegetação ou a regeneração da vegetação onde esta sofreu algum tipo de distúrbio (<span class="ref"><strong class="xref xrefblue">Brancalion <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Brancalion, H.S., Galdolfi, S., Rodrigues, R. R. 2015. Restauração Florestal. Oficina de Textos, São Paulo.</span></span></span>).</p>
+<p>Para cada fase da sucessão, em uma floresta secundária, há predomínio de determinadas espécies pertencentes a um grupo sucessional (<span class="ref"><strong class="xref xrefblue">Clements 1916</strong><span class="refCtt closed"><span>Clements, F.E. 1916. Plant succession: Na analysis of the development of vegetation. BHL: Biodiversity Heritage Library. Disponível em www.biodversitylibrary.org/ (acesso em 18-V-2020).</span><br><a href="www.biodversitylibrary.org/" target="_blank">www.biodversitylibrary.org/...
+            </a></span></span>). Segundo <span class="ref"><strong class="xref xrefblue">Whitmore (1989)</strong><span class="refCtt closed"><span>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</span></span></span>, o conhecimento sobre a substituição de espécies ao longo do processo de sucessão, é fundamental para avaliar o grau de maturidade em que se encontra um determinado fragmento florestal.</p>
+<p>Conforme a <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>tabela 1</a>, o primeiro estudo a classificar as espécies por suas respectivas categorias foi realizado por <span class="ref"><strong class="xref xrefblue">Budowski (1965)</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span>, este utilizou as categorias pioneira, secundária inicial, secundária tardia e clímax. Posteriormente, alguns autores classificaram as espécies de forma mais sucinta, ou seja, espécies pioneiras e não-pioneiras como: <span class="ref"><strong class="xref xrefblue">Gómez-Pompa (1971)</strong><span class="refCtt closed"><span>Gómez-Pompa, A. 1971. Posible papel de la vegetación secundaria en la evolución de la flora tropical. Biotropica 3: 125-135.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Whitmore (1989)</strong><span class="refCtt closed"><span>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>. Já, em outros estudos, os autores optaram por classificar as espécies separando as não pioneiras, por secundárias iniciais e secundárias tardias e as espécies típicas de sub-bosque ou conhecidas como umbrófilas.</p>
+<p>Portanto, conforme as análises dos estudos apresentados na <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>tabela 1</a>, as espécies pioneiras predominam no início da sucessão, podem ser encontradas em grandes clareiras, produzem sementes pequenas e abundantes, que necessitam de luz direta para germinar, além disso tem crescimento rápido e ciclo de vida curto; as espécies secundárias iniciais estabelecem-se em pequenas clareiras, assemelham-se às pioneiras quanto à necessidade de luz para germinar suas sementes, mas têm ciclo de vida mais longo; as secundárias tardias destacam-se na fase mais madura da floresta, suas sementes não necessitam de luz direta para germinar e são geralmente maiores, menos abundantes que as das espécies pioneiras, podem apresentar dormência e suas plântulas vivem na sombra, com crescimento lento e ciclo de vida longo; as espécies umbrófilas ou típicas de sub-bosque, estão presentes em todas as fases, mas com maior densidade na fase madura. O que as diferem das secundárias tardias é que em todo seu ciclo de vida se desenvolvem inteiramente no estrato inferior da floresta (<span class="ref"><strong class="xref xrefblue">Budowski 1965</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gómez-Pompa 1971</strong><span class="refCtt closed"><span>Gómez-Pompa, A. 1971. Posible papel de la vegetación secundaria en la evolución de la flora tropical. Biotropica 3: 125-135.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Swaine &amp; Whitmore 1988</strong><span class="refCtt closed"><span>Swaine, M.D. &amp; Whitmore, T.C. 1988. On the definition of ecological species groups in tropical rain forests. Vegetation 75: 81-86.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kageyama &amp; Castro 1989</strong><span class="refCtt closed"><span>Kageyama, P.Y. &amp; Castro, C.F.A. 1989. Sucessão secundária, Estrutura genética e Plantações de espécies arbóreas nativas. Instituto de Pesquisas e Estudos Florestais 41/42: 83-93.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gandolfi 1991</strong><span class="refCtt closed"><span>Gandolfi, F. 1991. Estudo florístico e fitossociológico de uma floresta residual na área do Aeroporto Internacional de São Paulo, Município de Guarulhos, SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. 2006</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>).</p>
+<p>No Estado de São Paulo, uma importante unidade de conservação é o Parque Estadual da Cantareira, localizado na região metropolitana da cidade de São Paulo, sendo um dos principais remanescentes florestais, formados por florestas secundárias em diferentes estágios sucessionais, porém mantendo alta riqueza de biodiversidade.</p>
+<p>Estudos sobre a dinâmica do processo sucessional em florestas do Planalto Paulista são escassos. Portanto, o presente estudo poderá fornecer contribuições para a temática e para aplicações práticas no âmbito local e regional.</p>
+<p>O objetivo deste estudo foi comparar quanto ao estágio sucessional, trechos da floresta do Parque Estadual da Cantareira através da análise de sua estrutura e espécies características de seus estratos, contribuindo para o conhecimento, conservação e a proteção das florestas secundárias urbanas.</p>
+<p>Para tanto elaboramos as seguintes perguntas:</p>
+<p>A. Como a composição florística e a estrutura variam nas áreas analisadas?</p>
+<p>B. É possível reconhecer estágios sucessionais diferentes nas áreas estudadas?</p>
+<p>C. Como as espécies de diferentes grupos sucessionais estão representadas nas áreas estudadas?</p>
+<h1 class="articleSectionTitle">Material e Métodos</h1>
+<p>Área de Estudo - O Parque Estadual da Cantareira (PEC) possui 7.916,5 hectares, abrangendo parte dos munícipios de Caieiras, Guarulhos, Mairiporã e São Paulo, na bacia do Alto Tietê, na Serra da Cantareira. Destaca-se entre seus serviços ecossistêmicos, a grande riqueza de mananciais que abriga em sua área (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>Essa região anteriormente é composta por fazendas de café, que foram adquiridas pelo governo do Estado, preocupado com o abastecimento de água. A captação de água na Serra da Cantareira iniciou-se em 1877. O abastecimento acontecia a partir de um sistema de pequenas represas, suficientes para abastecer a população que residia no centro da cidade com uma água de excelente qualidade. Com o aumento da urbanização, os mananciais da Serra da Cantareira deixaram de ser suficientes para o abastecimento da cidade de São Paulo. Atualmente, apenas uma parte do município de Guarulhos é abastecida pelos mananciais do PEC (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>Como resultado deste histórico, formou-se uma floresta secundária, onde predominam manchas em fases intermediárias de sucessão (<span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. 1993</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>O PEC é composto por 4 zonas administrativas: Núcleo Engordador, localizado entre os municípios de Mairiporã e São Paulo; Águas Claras, no município de Mairiporã; Cabuçu em Guarulhos e Pedra Grande, que abrange parte dos municípios de Caieiras, Mairiporã e São Paulo (<span class="ref"><strong class="xref xrefblue">Ayres 2006</strong><span class="refCtt closed"><span>Ayres, N.C.M. 2006. O ciclo da Caapora: Uma história de relação entre a RMSP e o Parque Estadual da Cantareira (1963 - 2005). São Paulo. Dissertação de Mestrado, Universidade Católica de São Paulo. São Paulo.</span></span></span>, <span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>A área de estudo está localizada no Núcleo Pedra Grande. Conforme o <span class="ref"><strong class="xref xrefblue">IBGE (2012)</strong><span class="refCtt closed"><span>IBGE. 2012. Fundação Instituto Brasileiro de geografia e Estatística. Manual técnico da vegetação brasileira. 2ed, Rio de Janeiro.</span></span></span>, a área é recoberta pela Floresta Ombrófila Densa Montana. De acordo com a classificação de Köppen, o clima é do tipo úmido, temperado e sem estação seca - Cfb (<span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>), ou seja, com precipitação média do mês mais seco &gt; 30 mm e a temperatura média do mês mais quente &lt;22ºC (<span class="ref"><strong class="xref xrefblue">Köppen 2019</strong><span class="refCtt closed"><span>Köppen, G. Classificação Climática de Koppen-Geiser. Disponível em https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf (acesso em 17-XI-2019).</span><br><a href="https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf" target="_blank">https://portais.ufg.br/up/68/o/Classific...
+            </a></span></span>). O relevo é montanhoso, com amplitudes de 120 a 400 metros e altitudes de 875 a 1215 metros (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<div class="row table" id="t1">
+<a name="t1"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 1</strong></strong><br> Classificação Sucessional adotada por alguns autores ao longo dos anos.<br><strong><strong>Table 1</strong></strong><br> Sucessional classification adopted by some authors over the years.<br>
+</div>
+</div>
+<p>Métodos - Para o presente estudo foram selecionadas três áreas amostrais de 0,2 ha cada, subdivididas em dez parcelas contíguas de 10 x 20 m, totalizando uma área amostral de 0,6 ha. A distância aproximada entre a área C e A é de 250 m e da área A para B de 400 m, com as respectivas localizações: área A (23°25’46”S, 46°38’6”O), área B (23°25’40”S, 46°37’54”O) e área C (23°25’53”S, 46°38’0”O) (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1"><span class="sci-ico-fileFigure"></span>figura 1</a>). As três áreas encontram-se afastadas das trilhas para se evitar o efeito de borda, como recomendado por <span class="ref"><strong class="xref xrefblue">Rodrigues &amp; Shepherd (1992)</strong><span class="refCtt closed"><span>Rodrigues, R.R. &amp; Shepherd, G.J. 1992. Análise da variação estrutural e fisionômica da vegetação e características edáficas, num gradiente altitudinal na Serra do Japi. In: L.P.C. Morellato (org.). História natural da Serra do Japi: ecologia e preservação de uma área florestal no sudeste do Brasil. Editora Unicamp: Campinas, pp. 64-96.</span></span></span> e possuem declividades semelhantes.</p>
+<p>Foram amostrados todos os indivíduos com PAP, perímetro do tronco à altura de 1,30 m acima do solo ≥ 15 cm. Os indivíduos mortos, mesmo em pé, não foram amostrados. A altura das árvores foi estimada utilizando-se tesoura de poda alta como referência. As amostras botânicas foram coletadas, herborizadas e identificadas por comparação com exsicatas depositadas em herbário, consultas a especialistas e bibliografias específicas. As amostras férteis foram registradas e incorporadas no Herbário Dom Bento Pickel (SPSF) do Instituto Florestal.</p>
+<p>Para a classificação das famílias, foi utilizado o Angiosperm Phylogeny Group - APG IV (<span class="ref"><strong class="xref xrefblue">APG - Angiosperm Phylogeny Group 2016</strong><span class="refCtt closed"><span>APG - Angiosperm Phylogeny Group. 2016. An update of the Angiosperm Phylogeny Group Classification for the orders and families of flowering plants: APG IV. Botanical Journal of the Linnean Society 181: 1-20.</span></span></span>). Os nomes científicos foram conferidos com a lista de espécies da Flora do Brasil (<span class="ref"><strong class="xref xrefblue">Flora do Brasil 2020 - em construção 2020</strong><span class="refCtt closed"><span>Flora do Brasil 2020 em construção. Jardim Botânico do Rio de Janeiro. Disponível em (http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964) (acesso em 11-III-2020).</span><br><a href="http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964" target="_blank">http://floradobrasil.jbrj.gov.br/reflora...
+            </a></span></span>).</p>
+<p>Os parâmetros fitossociológicos calculados nas análises foram: número de indivíduos (ni), densidade relativa (DR), dominância relativa (DoR), frequência relativa (FR), valor de cobertura (VC) e valor de importância (VI), segundo <span class="ref"><strong class="xref xrefblue">Mueller-Dombois &amp; Ellenberg (1974)</strong><span class="refCtt closed"><span>Mueller-Dombois, D. &amp; Ellenberg, H. 1974. Aims and methods of vegetation ecology. New York: John Wiley &amp; Sons.</span></span></span>. Também foram realizadas análises multivariadas de classificação e ordenação, utilizando-se matrizes de número de indivíduos, para verificar a eventual formação de grupos nas unidades amostrais da área de estudo e comparar as parcelas e blocos entre si. Nas análises de classificação, para comparação de matrizes de números de indivíduos, foram utilizados os métodos UPGMA - Unweighted Pair Group Method with Arithmetic Mean com coeficiente de Bray-Curtis. Como método de ordenação foi utilizado CA (Análise de Correspondência). Para esses cálculos e análises, foi utilizado o programa Fitopac 2.1 (<span class="ref"><strong class="xref xrefblue">Shepherd 2010</strong><span class="refCtt closed"><span>Shepherd, G. J. 2010. Fitopac 2.1. Manual do usuário. Campinas: UNICAMP.</span></span></span>).</p>
+<p>As espécies foram classificadas segundo o tipo de dispersão de seus propágulos, como zoocóricas, anemocóricas e autocóricas, de acordo com <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>); <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>.</p>
+<p>A apresentação das espécies ameaçadas deu-se pelas consultas às seguintes listas: IUCN (2020), nacional (Portaria MMA nº 443, de 17 de dezembro de 2014 - Brasil 2020) e estadual (Resolução SMA Nº 57, de 05 de junho de 2016 - <span class="ref"><strong class="xref xrefblue">São Paulo 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>).</p>
+<p>A classificação das espécies, segundo a categoria sucessional, foi baseada, principalmente, em observações de campo e em trabalhos realizados por <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>. Foram feitas duas classificações sucessionais, uma com quatro categorias: pioneiras, secundárias iniciais, secundárias tardias e umbrófilas, sendo as três primeiras conforme <span class="ref"><strong class="xref xrefblue">Budowski (1965)</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span> e, as umbrófilas, segundo <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span> e <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>; a segunda considerou as espécies como pioneiras e não-pioneiras (Secundárias iniciais, tardias e umbrófilas), adaptado de <span class="ref"><strong class="xref xrefblue">Barbosa (2017)</strong><span class="refCtt closed"><span>Barbosa, L.M. 2017. Lista de espécies indicadas para restauração ecológica para diversas regiões do Estado de São Paulo. Relatório Técnico, Secretaria do Meio Ambiente de São Paulo.</span></span></span>.</p>
+<p>Para auxiliar uma análise da distribuição das espécies em categoria sucessional, foram idealizados perfis diagramas totais de cada uma das áreas estudadas, com a representação dos indivíduos amostrados seguindo-se a sequência da planilha de campo, com núcleos diferentes segundo sua classificação sucessional.</p>
+<h1 class="articleSectionTitle">Resultados</h1>
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+<strong>Figura 1</strong><br>Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.<br><strong>Figure 1</strong><br>Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.<br>
+</div>
+</div>
+<p>Composição Florística - No levantamento geral, foram amostrados 1020 indivíduos, distribuídos em 115 espécies, 80 gêneros e 45 famílias (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>tabela 2</a>). A área B é mais rica, com 68 espécies, sendo 21% mais rica que C (56 spp.) e 26% mais rica que A (54 spp.).</p>
+<p>As famílias mais ricas em espécies foram Myrtaceae (17 espécies), Lauraceae (12), Fabaceae (8), Rubiaceae e Meliaceae (5). As famílias mais abundantes em indivíduos foram Euphorbiaceae (127 indivíduos), Myrtaceae (115), Olacaceae (114), Rubiaceae (108) e Meliaceae (68).</p>
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+<strong><strong>Tabela 2</strong></strong><br> Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.<br><strong><strong>Table 2</strong></strong><br> Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.<br>
+</div>
+</div>
+<p>Os gêneros mais ricos foram <i>Eugenia, Myrcia</i> e <i>Ocotea</i> (sete espécies cada), <i>Mollinedia</i> (quatro) e <i>Annona</i> e <i>Casearia</i> (três cada).</p>
+<p>Riqueza e Abundância nas Áreas A, B e C - Na Área A foram amostrados 321 indivíduos, 54 espécies e 26 famílias. As famílias com maior riqueza foram Myrtaceae (10 espécies), Lauraceae (6 esp.), Euphorbiaceae e Rubiaceae (4 esp.) e Monimiaceae (3 esp.). As famílias mais abundantes foram Rubiaceae (70 indivíduos), Olacaceae (42 ind.), Myrtaceae (32 ind.), Clusiaceae (23 ind.) e Monimiaceae (20 ind.). As famílias Rubiaceae e Olacaceae destacam-se nas primeiras posições quanto à abundância, não ocorrendo o mesmo em relação a riqueza, mostrando que a alta abundância dessas famílias é por causa de uma espécie, <i>Psychotria suterella</i> em Rubiaceae e <i>Heisteria silvianii</i> em Olacaceae. Os gêneros mais ricos foram <i>Myrcia</i> (quatro espécies), <i>Eugenia, Ocotea</i> e <i>Mollinedia</i> (três cada), <i>Annona</i> e <i>Cinnamomum</i> (duas cada). Podemos observar que dentre estas, somente <i>Cinnamomum</i> não se destacou nos resultados gerais.</p>
+<p>A Área B apresentou 399 indivíduos, 68 espécies e 32 famílias. As famílias com maior riqueza foram Myrtaceae (10 espécies), Lauraceae (7 esp.), Meliaceae (5 esp.), Sapindaceae e Monimiaceae (4 esp.).</p>
+<p>As famílias mais abundantes em número de indivíduos foram Myrtaceae (72 indivíduos), Sapindaceae (39 ind.), Meliaceae (38 ind.), Olacaceae (37 ind.) e Rubiaceae (31 ind.). Nesta área, Sapindaceae e Meliaceae, destacaram-se tanto no levantamento por espécies quanto de indivíduos. Os gêneros que se destacaram nesta área foram <i>Eugenia</i> (cinco espécies), <i>Mollinedia, Myrcia</i> e <i>Ocotea</i> (quatro espécies cada), também amostradas na área A, seguidas de <i>Casearia</i> (três) e <i>Matayba</i> (duas). Área C apresentou 300 indivíduos pertencentes a 56 espécies e 30 famílias. As famílias mais ricas foram Fabaceae (7 espécies), Lauraceae (6 esp.), Euphorbiaceae e Myrtaceae (4 esp.) e Meliaceae (2 esp.). As famílias Fabaceae e Euphorbiaceae também foram as mais ricas no levantamento realizado na Floresta Ombrófila Densa situada no município de Cunha - SP por <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span>. As famílias mais abundantes foram Euphorbiaceae (94 ind.), Olacaceae (35 ind.), Fabaceae (32 ind.), Meliaceae (16 ind.) e Lauraceae (15 ind). Em relação aos gêneros, aqueles que mais se destacaram nesta análise foram <i>Annona, Croton, Mollinedia, Myrcia, Myrsine, Nectandra, Ocotea</i> e <i>Vochysia</i> (duas espécies cada), sendo que as quatro primeiras destacadas acima, apresentaram-se somente nesta área.</p>
+<p>Ao compararmos as três áreas de estudo, Olacaceae destaca-se pela abundância nas três áreas, entretanto Myrtaceae e Rubiaceae em duas delas. A alta representatividade de Olacaceae é devida a uma única espécie, <i>H. silvianii</i>, e Rubiaceae por <i>P. suterella</i>, enquanto que Myrtaceae, pela riqueza de espécies. Em relação aos gêneros que mais se destacaram nas áreas estudadas, podemos observar que a área C foi aquela mais distinta dentre elas, pois nesta área não há uma predominância de um gênero.</p>
+<p>Parâmetros fitossociológicos - A <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>tabela 3</a> mostra os parâmetros totais e por área, a área B apresentou 39% do número total de indivíduos amostrados, enquanto as áreas A e C, 31% e 30% respectivamente.</p>
+<p>Na área A, <i>H. silvianii</i> (22,7%), <i>Aspidosperma olivaceum</i> (18,1%) e <i>Euplassa cantareirae</i> (10,4%), espécies secundárias tardias, apresentaram os maiores valores de dominância relativa. As espécies que destacaram pelo valor de densidade foram <i>P. suterella</i> (19,6%), <i>H. silvianii</i> (13,1%) e <i>Tovomitopsis paniculata</i> (7,1%).</p>
+<p>Na área B, as espécies <i>Alchornea triplinervia</i> (22,6%), <i>H. silvianii</i> (11,1%), <i>Cabralea canjerana</i> (6,8%), <i>Casearia obliqua</i> (6,5%) e <i>Platymiscium floribundum</i> (6,4%) destacaram-se por seus valores de dominância relativa. Dentre elas, <i>H. silvianii</i> é a única secundária tardia e também apresentou alto valor de dominância na área A. Destacaram-se pelo valor de densidade, <i>H. silvianii</i> (9,3%), <i>Cupania oblongifolia</i> (8,8%), <i>Myrcia tijucensis</i> (7,3%) e <i>P. suterella</i> (7,0%).</p>
+<p>Na área C, destacaram-se pelo valor de dominância <i>Piptadenia gonoacantha</i> (26,50%), <i>Croton floribundus</i> (24,8%), <i>A. triplinervia</i> (10,4%) e <i>Bauhinia forficata</i> (6,8%). Destacaram-se pelo valor de densidade, <i>C. floribundus</i> (18,0%), <i>H. silvianii</i> (11,67%), <i>A. triplinervia</i> (7,7%) e <i>P. gonoacantha</i> (6,7%).</p>
+<p>Ao comparar as três áreas de estudo pelas espécies presentes, podemos constatar que as três áreas amostradas apresentam estrutura e composição florística distintas. Algumas espécies aparecem nas três áreas, mas em situações diferentes, por exemplo, <i>H. silvianii,</i> destacou-se tanto na área A e B, por seu valor de dominância, enquanto na área C, pela frequência, mostrando que nas duas primeiras áreas encontra-se no dossel, enquanto em C, nos estratos inferiores da floresta.</p>
+<p>Ao comparar a densidade das três áreas, constatamos que B (1995 ind./ha) é a mais densa, sendo 33% maior que C (1500 ind./ha) e 24% maior que A (1605 ind./ha). A maior densidade da área B pode ser explicada pelo predomínio de secundárias iniciais no dossel e pela grande quantidade de secundárias tardias no sub-bosque, estas últimas, em fase de crescimento, com um grande número de indivíduos jovens com pequenos diâmetros. Ao tratar-se de dominância, o cenário muda, pois, a área C apresenta a menor dominância (30,6 m<sup>2</sup> /ha), em comparação com as áreas A e B (45,4 m<sup>2</sup>/ha e 43,4 m<sup>2</sup>/ha, respectivamente), sendo 32,5% e 29,4% menor, respectivamente, enquanto os valores da área A e B são próximos.</p>
+<p>Os valores de DeA e DoA mostram que na área A, há vários indivíduos com grandes diâmetros, mas estes pertencem a um mesmo grupo ecológico (secundárias tardias), indicando que a área está mais avançada na sucessão. Na área B, as espécies com os maiores diâmetros pertencem a mais de um grupo ecológico, principalmente as secundárias iniciais e algumas tardias, devido à maior riqueza e ao maior número de indivíduos. Na área C, a situação é bem distinta, pois tanto a DeA quanto a DoA tem valores baixos, quando comparados com A e B, indicando um maior número de indivíduos com diâmetros menores.</p>
+<p>Análises grupos ecológicos - Na análise total de espécies, quanto aos seus respectivos grupos ecológico, as secundárias tardias e iniciais mantiveram-se em proporções próximas (33,9% e 29,6%, respectivamente), as umbrófilas com 20% e, as pioneiras, de menor riqueza de espécies, com 16,5%. Ao realizarmos as mesmas análises, com o número de indivíduos, os resultados permaneceram similares. Na análise por espécies pioneiras ou não-pioneiras, 46,1% são espécies pioneiras e 53,9% não-pioneiras e, analisando pelo número de indivíduos, 39,5% e 60,5% respectivamente, observando resultados diferentes.</p>
+<p>Na área A, as espécies secundárias tardias destacaram-se com 48,1% do total de espécies, seguidas das iniciais com 25,9%, umbrófilas com 22,2% e, por fim, as pioneiras com 3,7% (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>figuras 2 a, b</a>). Nas mesmas análises com o número de indivíduos, o que se diferenciou foram as espécies umbrófilas, apresentando aumento de 13,7%, em função da riqueza da espécie <i>P. suterella</i>. E o oposto ocorreu com as iniciais, pois houve uma diminuição de 11,3%. Na análise de espécies classificadas como pioneiras ou não pioneiras, a porcentagem foi de 70,4% e 29,6%, respectivamente, enquanto abundância das espécies não-pioneiras foi 84,4% e pioneiras, 15,6%, do total de indivíduos amostrados. Esses resultados mostram que as espécies pertencentes ao grupo das pioneiras não são muito representadas pelo número de indivíduos.</p>
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+<strong><strong>Tabela 3</strong></strong><br> Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong><strong>Table 3</strong></strong><br> Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na área B, tanto as secundárias iniciais quanto as tardias apresentaram 35,3% do total de espécies, em seguida, as espécies umbrófilas com 22,1% e, as pioneiras, com 7,3%. Nas análises apresentadas pelo número de indivíduos não ocorreram grandes modificações, secundárias tardias com 37,1%, iniciais, 35,1%, umbrófilas, 26,6%, e as pioneiras, 1,2%. Na análise quanto a pioneiras e não pioneiras, a riqueza de espécies não-pioneiras foi 57,3%, e pioneiras, 42,6%. Quanto ao número de indivíduos, as não-pioneiras apresentaram 63,7% e as pioneiras 36,3% (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>figuras 3 a, b</a>). Esses resultados são semelhantes quando comparamos as duas classificações sucessionais. Nesta área há maior número de pioneiras em relação à área A.</p>
+<p>Na área C, as espécies secundárias iniciais ainda predominam, com 32,1%, em seguida estão as espécies pioneiras, com 28,57%, as secundárias tardias, com 21,4% e, as umbrófilas, com 17,9%. Nas análises de abundância, as pioneiras predominam com 40%, secundárias iniciais, 29,3%, tardias, 19,7%, e umbrófilas, 11%. Nesta área ocorre o oposto das outras duas áreas, pois as pioneiras se destacam, sendo essa diferença mais expressiva nas análises por abundância. As espécies pioneiras apresentaram 60,7% do total de espécies e as não-pioneiras 39,3%. Já a abundância de pioneiras e não pioneiras foi 69,3% e 30,7% respectivamente (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf4"><span class="sci-ico-fileFigure"></span>figuras 4 a, b</a>). De modo geral, essa área se diferencia das outras não só pelo aumento das espécies que sobrevivem em condições de luz, mas também a diminuição das espécies que vivem sobre condições de sombra, mostrando assim, que se trata de uma área mais aberta, com dossel mais falho, facilitando a presença de luz direta no solo.</p>
+<p>Na área A as espécies secundárias tardias destacam-se pela dominância, densidade e riqueza, revelando que as espécies desse estágio estão fortemente presentes no dossel da floresta como também nos estratos inferiores.</p>
+<p>Na área B as espécies secundárias iniciais destacam-se pela dominância, porém, nos parâmetros densidade e riqueza, as iniciais se igualam com as tardias. Esses resultados mostram que o dossel nessa área é composto, principalmente, pelas iniciais. Nos estratos inferiores os dois grupos estão fortemente presentes.</p>
+<div class="row fig" id="f2">
+<a name="f2"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf2"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 2</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 2</strong><br>a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na área C ocorre o oposto, pois, as espécies pioneiras destacam-se pela dominância, mostrando que nesse trecho as pioneiras estão presentes no dossel, porém nos parâmetros de densidade e riqueza, as pioneiras perdem o pódio, dando lugar para as espécies secundárias e umbrófilas.</p>
+<p>As espécies umbrófilas aumentam da área C para A, indicando que a área A está em fase mais avançada de sucessão, aumentando a predominância das espécies típicas de sub-bosque neste estrato (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf5"><span class="sci-ico-fileFigure"></span>figuras 5 a, b, c</a>).</p>
+<p>Em complemento à análise da classificação sucessional, foram elaborados perfis diagramas totais de cada uma delas, com a representação dos indivíduos amostrados seguindo a sequência da planilha de campo. Os indivíduos indicados na coloração amarela são representados pelas pioneiras; verdes claras, secundárias iniciais; verdes escuras, tardias; e as vermelhas, espécies umbrófilas.</p>
+<p>Na área A, o dossel é predominantemente composto pelas tardias, no estrato intermediário predominam as iniciais, enquanto no sub-bosque predominam espécies umbrófilas. Ocorreram três indivíduos de espécies pioneiras, desses, dois no estrato intermediário em direção ao dossel e um no sub-bosque (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf6"><span class="sci-ico-fileFigure"></span>figura 6</a>).</p>
+<p>Na área B, predominam secundárias iniciais no dossel; no estrato intermediário, além das iniciais, também ocorrem as tardias; o sub-bosque têm representantes de todos os grupos sucessionais, mas com baixa representatividade das pioneiras, com apenas cinco indivíduos (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf7"><span class="sci-ico-fileFigure"></span>figura 7</a>).</p>
+<p>Na área C, há predomínio das pioneiras no dossel, cuja altura é mais baixa que A e B. Já no estrato intermediário predominam pioneiras e secundárias iniciais e, no sub-bosque, estão presentes espécies pioneiras, secundárias iniciais e tardias, havendo poucas espécies umbrófilas (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf8"><span class="sci-ico-fileFigure"></span>figura 8</a>).</p>
+<p>De modo geral, observa-se que as três áreas são distintas, pois, na área A, as espécies estão distribuídas conforme o esperado para um final de sucessão, com o predomínio das secundárias tardias no dossel; já na área B, ocorre o predomínio das secundárias iniciais no dossel e, nos outros estratos, há todos os grupos sucessionais presentes, resultando em um grande número de indivíduos e, na área C, as pioneiras estão bem representadas em todos os estratos.</p>
+<div class="row fig" id="f3">
+<a name="f3"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf3"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 3</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 3</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f4">
+<a name="f4"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf4"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 4</strong><br>a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 4</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Com base na distribuição dos grupos sucessionais, a área A está em estágio mais avançado ou final na sucessão, a área B em um estágio intermediário e, área C, em estágio mais inicial.</p>
+<p>Estratificação florestal e distribuição diamétrica - Na área A, aproximadamente 64% (204) dos indivíduos amostrados apresentam até 12 m de altura, 17% (59 ind.) entre 12,1 e 20 m, 15% entre 20,1 e 28 m e 4% entre 28,1 e 36 m (21 ind.). Essa distribuição de indivíduos apresenta formato de “J invertido” (maior número de indivíduos nas menores classes de altura, diminuindo nas maiores classes). A grande concentração de indivíduos na primeira classe de altura deve-se pela abundância das espécies umbrófilas, principalmente <i>P. suterella</i> (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf9"><span class="sci-ico-fileFigure"></span>figura 9</a>).</p>
+<p>Na área B, aproximadamente 59% (238) dos indivíduos amostrados apresentam até 12 m de altura, 25% (102 ind.) entre 12,1 e 20 m, 12% entre 20,1 e 28 m. e 4% entre 28,1 e 36 m (59 ind.). Poucos indivíduos passam dos 30 metros de altura (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf10"><span class="sci-ico-fileFigure"></span>figura 10</a>).</p>
+<p>Já na área C, aproximadamente 65% (196) dos indivíduos amostrados apresentam até 12 m de altura, 28% (83 ind.) entre 12,1 e 20 m. e 7% (21 ind.) acima dos 20 m. (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf11"><span class="sci-ico-fileFigure"></span>figura 11</a>).</p>
+<p>Ao compararmos as três áreas de estudo, quanto à distribuição das classes de altura, podemos constatar que as áreas A e B são similares quanto à porcentagem dos indivíduos em diferentes estratos. Em ambas as áreas há a predominância das secundárias tardias e iniciais nos diferentes estratos, com exceção do sub-bosque que em A possui exclusivamente espécies deste estrato (umbrófilas), enquanto em B ocorrem também indivíduos jovens de espécies secundárias. Por outro lado, na área C, a porcentagem dos indivíduos na classe até 12 m de altura é bem menor em relação às áreas A e B; as espécies pioneiras estão representadas em todos os estratos dessa floresta e, no sub-bosque há representantes de todas as categorias sucessionais.</p>
+<p>Similaridade, agrupamento e ordenação entre as áreas de estudo - Na análise utilizando o coeficiente Canberra (UPGMA), as parcelas de um mesmo bloco mantêm-se de uma forma geral em um mesmo grupo, confirmando que as áreas de estudo (A, B e C) diferem entre si. No primeiro grupo, onde se encontram as parcelas da área A, há somente uma única parcela (12) que pertence a B; porém o segundo e o terceiro grupos reconhecidos nesta análise reúnem exclusivamente parcelas das áreas B e C respectivamente (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf12"><span class="sci-ico-fileFigure"></span>figura 12</a>). O agrupamento da parcela 12 (área B) com as parcelas 1 a 10 (área A), pode ser explicada como uma parcela cuja floresta está em fase mais final de sucessão. É comum nas florestas ter parcelas em fases distintas, podendo ser causadas pela presença de uma mancha mais antiga, clareiras ou efeitos de borda. As análises de ordenação e classificação mostram esses efeitos.</p>
+<div class="row fig" id="f5">
+<a name="f5"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf5"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 5</strong><br>a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br><strong>Figure 5</strong><br>a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f6">
+<a name="f6"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf6"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 6</strong><br>Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 6</strong><br>Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f7">
+<a name="f7"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf7"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 7</strong><br>Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 7</strong><br>Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na análise de ordenação, utilizou-se a Análise de Correspondência (CA) e a matriz de número de indivíduos por espécie. Os eixos 1, 2 e 3 correspondem a 11,8, 8,5 e 6,1 por cento da inércia total encontrada, totalizando-se 26,4%. Podemos observar que as parcelas da área C estão separadas em todos os eixos (plano horizontal e vertical), sendo esta a mais diferente em relação às demais. As áreas A e B estão separadas mais no eixo 2 (plano horizontal), ou seja, em relação ao número de indivíduos, estão mais próximas, possivelmente devido às espécies tardias já estarem presentes nos estratos inferiores da área B (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf13"><span class="sci-ico-fileFigure"></span>figuras 13</a> to <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf14"><span class="sci-ico-fileFigure"></span>14</a>).</p>
+<p>Tanto as análises de classificação quanto as de ordenação mostram, de uma forma geral, a formação de três grupos que correspondem às três áreas de estudo, havendo maior proximidade entre as áreas A e B devido a uma maior presença das espécies tardias em ambas as áreas.</p>
+<p>Síndrome de dispersão - As espécies zoocóricas destacaram-se em todas as áreas estudadas, A, B e C (85%, 88% e 70%, respectivamente). As anemocóricas apresentaram valores mais altos na área C, em virtude do maior número de pioneiras encontradas nesta última. Já as autocóricas estão em menor número na área B.</p>
+<p>Espécies ameaçadas de extinção - Do total de 115 espécies apuradas neste estudo, conforme consta na <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>tabela 4</a>, sete espécies (6,1%) enquadram-se em uma das categorias de grau de ameaça nas três listas existentes. <i>Ocotea catharinensis,</i> presente nas três áreas de estudo, está como vulnerável (VU) nas listas de São Paulo, do Brasil e IUCN; <i>Cedrela fissilis</i>, presente somente na área B, apresentou-se como VU nas listas de São Paulo e do Brasil, e em perigo (EN) na lista da IUCN; <i>Trichilia silvatica</i>, presente nas áreas A e B, e <i>Eugenia prasina</i>, na área B, estão representadas como VU somente na lista da IUCN; <i>Virola bicuhyba</i> presente somente na área B, encontra-se EN nas listas de São Paulo e do Brasil; <i>Pouteria bullata</i>, presente somente na área B, é considerada EN na lista de São Paulo e Brasil e VU na lista da IUCN; <i>E. cantareirae</i> presente somente na área A, na lista do Brasil está como EN e na lista de São Paulo está como extinta (EX).</p>
+<div class="row fig" id="f8">
+<a name="f8"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf8"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 8</strong><br>Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 8</strong><br>Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f9">
+<a name="f9"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf9"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 9</strong><br>Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 9</strong><br>Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<h1 class="articleSectionTitle">Discussão</h1>
+<p>Composição Florística - As famílias Myrtaceae e Lauraceae também foram as mais ricas em outros estudos realizados na Floresta Ombrófila Densa Montana no Estado de São Paulo por <span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. (1993)</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Garcia &amp; Pirani (2001)</strong><span class="refCtt closed"><span>Garcia, R.J.F. &amp; Pirani, J.R. 2001. Estudo florístico dos componentes arbóreos e arbustivo da mata do Parque Santo Dias, São Paulo, SP, Brasil. Boletim de Botânica Universidade de São Paulo 19: 15-42.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Alves &amp; Metzger (2006)</strong><span class="refCtt closed"><span>Alves, L.F. &amp; Metzger, J.P. 2006. A regeneração florestal em áreas de floresta secundária na Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Ogata &amp; Gomes (2006)</strong><span class="refCtt closed"><span>Ogata, R. &amp; Gomes, E.P.C. Estrutura e composição da vegetação no Parque CEMUCAM, Cotia, SP. Hoehnea 33(3): 371-384.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, trabalhos realizados no município de São Paulo e arredores, e no interior do Estado, por <span class="ref"><strong class="xref xrefblue">Ivanauskas (1997)</strong><span class="refCtt closed"><span>Ivanauskas, N. M. 1997. Caracterização florística e fisionômica da Floresta Atlântica sobre a formação Pariquera-Açu, na Zona da Morraria Costeira do Estado de São Paulo. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Sztutman &amp; Rodrigues (2002)</strong><span class="refCtt closed"><span>Sztutman, M. &amp; Rodrigues, R.R. 2002. O mosaico vegetacional numa área de floresta contínua da planície litorânea, Parque Estadual da Campina do Encantado, Pariquera-Açu, SP. Revista Brasileira de Botânica 25(2): 161-176.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>, sendo que neste último estudo somente Myrtaceae destacou-se pela sua riqueza.</p>
+<p>Os gêneros <i>Cinnamomum, Eugenia, Mollinedia, Myrcia</i> e <i>Ocotea</i> também se destacaram em outros levantamentos realizados no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>), <i>Nectandra</i> também se destacou no levantamento realizado no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <i>Eugenia, Myrcia</i> e <i>Ocotea</i>, por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span> em remanescentes de Floresta Ombrófila Densa Montana situados na região metropolitana de São Paulo, <i>Eugenia</i> e <i>Ocotea,</i> por <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span> na região de Cunha e somente <i>Eugenia</i> por <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> no município de Miracatu.</p>
+<div class="row fig" id="f10">
+<a name="f10"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf10"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 10</strong><br>Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 10</strong><br>Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f11">
+<a name="f11"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf11"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 11</strong><br>Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 11</strong><br>Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Parâmetros fitossociológicos - Os valores totais, desde estudo, de densidade absoluta de 1700 ind. ha<sup>-1</sup> e dominância absoluta de 39,8 m<sup>2</sup> ha<sup>-1</sup> são compatíveis com os encontrados em outros trechos do PEC (<span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. 1993</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>), onde a densidade absoluta variou entre 1248 a 2295 ind./ha e a dominância entre 35,7 a 48,4 m<sup>2</sup> ha<sup>-1</sup>. Em estudo realizado em São Paulo e nos municípios vizinhos de Cotia e Itapevi (<span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>) os valores de densidade variaram entre 1425 a 1760 ind. ha<sup>-1</sup> e de dominância entre 44,5 a 49,3 m<sup>2</sup> ha<sup>-1</sup>, também compatíveis com os do presente estudo.</p>
+<p>Em outros trechos da floresta do PEC estudados por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, também foram encontradas <i>H. silvianii</i> e <i>A. olivaceum</i> entre as espécies mais dominantes, e em Itapevi, somente <i>H. silvianii</i> (<span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>). <span class="ref"><strong class="xref xrefblue">Klein (1990)</strong><span class="refCtt closed"><span>Klein, R.M. 1990. Estrutura, composição florística, dinamismo e manejo da Mata Atlântica (Floresta Ombrófila Densa) do Sul do Brasil. In: Simpósio de Ecossistemas da Costa Sul e Sudeste Brasileira: Estrutura, funções e manejo, 2 Águas de Lindóia, 1990. Anais... Academia de Ciências do Estado de São Paulo. pp. 259-286.</span></span></span> destaca <i>A. olivaceum</i> como uma das espécies mais importantes nas encostas das Serras do Sul do país e cita que <i>E. cantareirae</i> está associada a florestas em sucessão avançada. Sendo que esta também se destacou no estudo realizado no PEC por <span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. (1993)</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>. Ainda, <span class="ref"><strong class="xref xrefblue">Blum &amp; Roderjan (2007)</strong><span class="refCtt closed"><span>Blum, C.T. &amp; Roderjan, C.V. 2007. Espécies indicadoras em um gradiente da Floresta Ombrófila na Serra da Prata, Paraná, Brasil. Revista Brasileira de Biociências 5(2): 873-875.</span></span></span> citam a <i>E. cantareirae</i> como espécie indicadora de formação de Floresta Ombrófila Densa Montana.</p>
+<p>A espécie <i>P. suterella</i> também se destacou em outros fragmentos do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e na Floresta Ombrófila Densa Montana das encostas de Paranapiacaba (<span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. 2011</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>), sendo que <span class="ref"><strong class="xref xrefblue">Bertani (2006)</strong><span class="refCtt closed"><span>Bertani, D. F. 2006. Ecologia de populações de Psychotria suterella Müll. Arg. (Rubiaceae) em uma paisagem fragmentada de Mata Atlântica. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> relata que essa espécie frequentemente se destaca pelo seu valor de densidade nos fragmentos florestais do Estado de São Paulo.</p>
+<p><i>A. triplinervia, H. silvianii, C. canjerana, C. obliqua</i> e <i>P. floribundum</i> destacaram-se por seus valores de dominância em outros trechos do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>). Em alguns levantamentos realizados no Estado de São Paulo, <i>A. triplinervia</i> destacou-se pelo seu valor de importância (<span class="ref"><strong class="xref xrefblue">Ivanauskas 1997</strong><span class="refCtt closed"><span>Ivanauskas, N. M. 1997. Caracterização florística e fisionômica da Floresta Atlântica sobre a formação Pariquera-Açu, na Zona da Morraria Costeira do Estado de São Paulo. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>). Esta espécie ocorre somente na forma de indivíduos mais velhos nas florestas mais maduras, geralmente esparsos, sendo, por isso, rara, pois não se vê na regeneração (<span class="ref"><strong class="xref xrefblue">Klein 1984</strong><span class="refCtt closed"><span>Klein, R.M. 1984. Aspectos Dinâmicos da Vegetação do Sul do Brasil. Sellowia 36: 5-54.</span></span></span>, <span class="ref"><sup class="xref xrefblue">1990</sup><span class="refCtt closed"><span>Klein, R.M. 1990. Estrutura, composição florística, dinamismo e manejo da Mata Atlântica (Floresta Ombrófila Densa) do Sul do Brasil. In: Simpósio de Ecossistemas da Costa Sul e Sudeste Brasileira: Estrutura, funções e manejo, 2 Águas de Lindóia, 1990. Anais... Academia de Ciências do Estado de São Paulo. pp. 259-286.</span></span></span>). Na área de estudo, não foram observados indivíduos jovens desta espécie. No levantamento realizado por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, dentre essas espécies, somente <i>C. obliqua</i> se assemelha com este estudo.</p>
+<div class="row fig" id="f12">
+<a name="f12"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf12"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 12</strong><br>Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.<br><strong>Figure 12</strong><br>Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.<br>
+</div>
+</div>
+<div class="row fig" id="f13">
+<a name="f13"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf13"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 13</strong><br>Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 13</strong><br>Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f14">
+<a name="f14"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf14"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 14</strong><br>Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 14</strong><br>Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p><i>C. oblongifolia</i> destacou-se nos levantamentos de <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>. Em outro trecho estudado por <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <i>C. floribundus</i> e <i>A. triplinervia</i> também se destacaram. <i>Piptocarpha macropoda</i> também foi encontrada em alta frequência em trecho do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2011</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e no levantamento feito por <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> na Floresta Ombrófila Densa do Vale do Ribeira</p>
+<p>Análises grupos ecológicos - No estudo realizado por <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, em seu levantamento geral de espécies tardias, a percentagem apresentou o dobro do que encontrado neste estudo. Mas essa diferença pode ser pelo fato de que o autor considerou as espécies umbrófilas como parte das secundárias tardias.</p>
+<p>Em outro estudo realizado no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, as tardias destacaram-se três vezes a mais que as iniciais, mas lembrando que o autor considerou também naquele trabalho, assim como Barretto, as umbrófilas como parte das espécies tardias.</p>
+<p>O trabalho realizado por <span class="ref"><strong class="xref xrefblue">Gandolfi <i>et al</i>. (1995)</strong><span class="refCtt closed"><span>Gandolfi, F., Leitão-Filho, H.F., Bezerra, C.L.F. 1995. Levantamento florístico e caráter sucessional das espécies arbustivo-arbóreas de uma floresta mesófila semidecidua no município de Guarulhos, SP. Revista Brasileira Biologia 55(4): 753-767.</span></span></span>, apresentou 30% de espécies pioneiras, sugerindo que o trecho estudado pelo autor se encontrava numa condição inicial em termos sucessionais. Nos estudos de <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>, as pioneiras também obtiveram percentagem expressivas (61% e 26%, respectivamente), mas os trechos referem-se a áreas de regeneração.</p>
+<p><span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, em suas análises, constatou nas três áreas estudadas por ele, em fase avançada de sucessão, alta dominância e riqueza das espécies secundárias tardias, assim como observado na área A deste estudo.</p>
+<p>Síndrome de dispersão - Em outros levantamentos realizados na Floresta Ombrófila Densa por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al.</i> (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al.</i> (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> foram encontrados resultados semelhantes quanto à porcentagem de espécies zoocóricas. <span class="ref"><strong class="xref xrefblue">Lima <i>et al.</i> (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span> relata que nas áreas que desenvolveu seu estudo predominam espécies zoocóricas, sendo áreas maduras da Floresta Ombrófila Densa Montana das encostas da Serra do Mar em Santo André, e <span class="ref"><strong class="xref xrefblue">Mantovani (1998)</strong><span class="refCtt closed"><span>Mantovani, W. 1998. Dinâmica da Floresta Pluvial Atlântica. Anais do IV Simpósio de Ecossistemas Brasileiros. Praia, Represa e Mata - Águas de Lindóia. ACIESP 104 v. II.</span></span></span> relata que é comum a predominância de espécies zoocóricas nessas florestas.</p>
+<p>Espécies ameaçadas de extinção - A espécie <i>E. cantareirae</i> foi classificada como vulnerável (VU) no estudo realizado por <span class="ref"><strong class="xref xrefblue">Souza <i>et al</i>. (2016)</strong><span class="refCtt closed"><span>Souza, S.C.P.M., Silva, A.G., Franco, G.A.D.C., Ivanauskas, N.M. 2016. A vegetação secundária em um fragmento florestal urbano: Influência de exóticas invasoras na comunidade vegetal. Revista do Instituto Florestal 28(1): 7-35.</span></span></span>, o que diverge com a lista atualizada de flora ameaçada do Estado de São Paulo, publicada no Diário Oficial de São Paulo - Poder Executivo - Seção I - de 07 de junho de 2016, na qual consta como extinta (EX). Essa espécie é considerada rara, no entanto tal classificação para São Paulo necessita ser revista. A presença dessas espécies mostra a importância de se conservar e cuidar desse remanescente florestal.</p>
+<h1 class="articleSectionTitle">Conclusões</h1>
+<p>Dentre as conclusões deste estudo, podemos constatar que as três áreas analisadas são floristicamente e estruturalmente diferentes, pois algumas das espécies amostradas estão presentes em todas as áreas e outras são exclusivas em apenas uma ou duas delas e mesmo quando presentes nas três áreas, não apresentam o mesmo VI em cada uma delas.</p>
+<p>Todos os grupos sucessionais (pioneiras, secundárias iniciais e tardias e umbrófilas) estão presentes nas três áreas, porém em proporções distintas e também predominando variadamente em cada um de seus estratos.</p>
+<p>Na área A, em seu dossel, há predominância de espécies secundárias tardias; estrato médio com secundárias iniciais e o sub-bosque, majoritariamente, formado por espécies umbrófilas. Esta área ainda contem baixa representatividade de espécies pioneiras e secundárias iniciais que ocorrem em pequenas clareiras e bordas da mancha estudada.</p>
+<p>Na área B, as espécies secundárias iniciais predominam tanto no dossel quanto no estrato médio da floresta e o sub-bosque é formado por todos os grupos sucessionais, exceto as pioneiras, estas com baixa representatividade e, quando presentes, estão restritas a pequenas clareiras, o mesmo que ocorre na área A.</p>
+<div class="row table" id="t4">
+<a name="t4"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 4</strong></strong><br> Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.<br><strong><strong>Table 4</strong></strong><br> List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.<br>
+</div>
+</div>
+<p>A área C possui dossel descontínuo com predomínio de pioneiras; o estrato médio apresenta predomínio de pioneiras e iniciais, mas com poucas tardias e umbrófilas. As clareiras dessa área são maiores que em A e B. As espécies pioneiras compõem o dossel desta floresta.</p>
+<p>Conclui-se, pela análise, que a área A está em processo de sucessão mais avançado ou final, a área B em fase intermediária e, a C, em uma fase mais inicial das anteriores.</p>
+<p>Avaliar o estágio successional de uma determinada área é um grande desafio científico, com importantes implicações na conservação. Conhecer a floresta em diferentes estágios traz subsídios a medidas aplicadas visando a recuperação, não somente do Parque Estadual da Cantareira, como da Serra da Cantareira e demais áreas da Floresta Ombrófila Densa Montana. A floresta do Parque Estadual da Cantareira, especificamente no Núcleo Pedra Grande, apesar de haver sofrido grande pressão antrópica, ainda abriga remanescentes florestais preservados, dos quais a área A é um exemplo, que servem como fonte de sementes e outras unidades de dispersão para a recuperação natural dos trechos em estágio sucessional em fases intermediária a inicial, como as áreas B e C do presente estudo.</p>
+<p>Estudos de recuperação natural da vegetação nativa em florestas do Planalto Paulista além de serem escassos, são de grande importância para garantir às gerações futuras a manutenção dos serviços ecossistêmicos da Floresta Ombrófila Densa, a Mata Atlântica, hoje ainda bastante afetada pela fragmentação e consequente perda de biodiversidade.</p>
+</div>
+<div class="articleSection" data-anchor="Agradecimentos">
+<h1 class="articleSectionTitle">Agradecimentos</h1>
+<p>Agradecemos ao Conselho Nacional de Desenvolvimento Científico e Tecnológico, pela Bolsa de Mestrado concedida à primeira Autora (Processo nº 133843/2018-9) junto ao Programa de Pós-Graduação em Biodiversidade Vegetal e Meio Ambiente do Instituto de Botânica de São Paulo.</p>
+</div>
+<div class="articleSection" data-anchor="Literatura Citada">
+<h1 class="articleSectionTitle">Literatura Citada</h1>
+<div class="ref-list"><ul class="refList">
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+<li><div>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</div></li>
+<li><div>Mueller-Dombois, D. &amp; Ellenberg, H. 1974. Aims and methods of vegetation ecology. New York: John Wiley &amp; Sons.</div></li>
+<li><div>Myers, N., Mittermeier, R.A., Mittermeier, C.G., Fonseca, G.A.B. 2000. Kent, J. Biodiversity hotspots for conservation priorities. Nature 403: 853-845.</div></li>
+<li><div>Ogata, R. &amp; Gomes, E.P.C. Estrutura e composição da vegetação no Parque CEMUCAM, Cotia, SP. Hoehnea 33(3): 371-384.</div></li>
+<li><div>Polisel, R.T. &amp; Franco, G.A.D.C. 2007. Caracterização sucessional de uma floresta secundária com 40 anos de idade em Juquitiba, SP. Revista Brasileira de Biociências 5(supl. 2): 387-389.</div></li>
+<li><div>Rocha, A.A. &amp; Costa, J.P.O. 1998. A Reserva da Biosfera da Mata Atlântica e sua aplicação no Estado de São Paulo: apresentação Covas, M.; prefácio Feldmann, F. J. - São Paulo: Terra Virgem, Secretaria do Meio Ambiente do Estado de São Paulo.</div></li>
+<li><div>Rodrigues, R.R. &amp; Shepherd, G.J. 1992. Análise da variação estrutural e fisionômica da vegetação e características edáficas, num gradiente altitudinal na Serra do Japi. <i>In</i>: L.P.C. Morellato (org.). História natural da Serra do Japi: ecologia e preservação de uma área florestal no sudeste do Brasil. Editora Unicamp: Campinas, pp. 64-96.</div></li>
+<li><div>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</div></li>
+<li><div>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</div></li>
+<li><div>Shepherd, G. J. 2010. Fitopac 2.1. Manual do usuário. Campinas: UNICAMP.</div></li>
+<li><div>Souza, S.C.P.M., Silva, A.G., Franco, G.A.D.C., Ivanauskas, N.M. 2016. A vegetação secundária em um fragmento florestal urbano: Influência de exóticas invasoras na comunidade vegetal. Revista do Instituto Florestal 28(1): 7-35.</div></li>
+<li><div>Swaine, M.D. &amp; Whitmore, T.C. 1988. On the definition of ecological species groups in tropical rain forests. Vegetation 75: 81-86.</div></li>
+<li><div>Sztutman, M. &amp; Rodrigues, R.R. 2002. O mosaico vegetacional numa área de floresta contínua da planície litorânea, Parque Estadual da Campina do Encantado, Pariquera-Açu, SP. Revista Brasileira de Botânica 25(2): 161-176.</div></li>
+<li><div>Tabarelli, M. 1994. Clareiras naturais e a dinâmica sucessional de um trecho de floresta na Serra da Cantareira, SP. Dissertação Mestrado, Universidade de São Paulo, São Paulo.</div></li>
+<li><div>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</div></li>
+</ul></div>
+</div>
+<div class="articleSection" data-anchor="Datas de Publicação ">
+<h1 class="articleSectionTitle">Datas de Publicação </h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Publicação nesta coleção</strong><br>24 Jan 2022</li>
+<li>
+<strong>Data do Fascículo</strong><br>2022</li>
+</ul></div></div>
+</div>
+<div class="articleSection" data-anchor="Histórico">
+<h1 class="articleSectionTitle">Histórico</h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Recebido</strong><br>13 Out 2020</li>
+<li>
+<strong>Aceito</strong><br>03 Nov 2021</li>
+</ul></div></div>
+</div>
+<section class="documentLicense"><div class="container-license"><div class="row">
+<div class="col-sm-3 col-md-2"><a href="http://creativecommons.org/licenses/by/4.0/" target="_blank" title=""><img src="https://licensebuttons.net/l/by/4.0//88x31.png" alt="Creative Common - by 4.0 "></a></div>
+<div class="col-sm-9 col-md-10"><a href="http://creativecommons.org/licenses/by/4.0/" target="_blank" title="">Este é um artigo publicado em acesso aberto (Open Access) sob a licença Creative Commons Attribution, que permite uso, distribuição e reprodução em qualquer meio, sem restrições desde que o trabalho original seja corretamente citado.</a></div>
+</div></div></section></article>
+</div>
+</div></div></section><div class="modal fade ModalDefault ModalTutors" id="ModalTutors" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Sobre os autores</h4>
+</div>
+<div class="modal-body">
+<div class="info">
+<div class="tutors">
+<strong> Rafaela Dias Valeck da Silva </strong><strong>4</strong><br><div>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-9049-3704" class="btnContribLinks orcid">http://orcid.org/0000-0002-9049-3704</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Inês Cordeiro </strong><br><div>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2626-5280" class="btnContribLinks orcid">http://orcid.org/0000-0002-2626-5280</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Frederico Alexandre Roccia Dal Pozzo Arzolla </strong><br><div>Instituto Florestal, Rua do Horto, 931, 02377-000 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0003-3111-6877" class="btnContribLinks orcid">http://orcid.org/0000-0003-3111-6877</a></li></ul>
+<div class="clearfix"></div>
+</div>
+</div>
+<div class="info"><div>Editora Associada: Cláudia Baider</div></div>
+<div class="info">1<div>Parte da Dissertação de Mestrado do primeiro Autor</div>
+</div>
+<div class="info">4 Autora para correspondência: <a href="mailto:rafaela_valeck@hotmail.com">rafaela_valeck@hotmail.com</a>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Figuras | Tabelas</h4>
+</div>
+<div class="modal-body">
+<ul class="nav nav-tabs md-tabs" role="tablist">
+<li role="presentation" class="col-md-4 col-sm-4 active"><a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">Figuras
+                    (14)
+                </a></li>
+<li role="presentation" class="col-md-4 col-sm-4 "><a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">Tabelas
+                    (4)
+                </a></li>
+</ul>
+<div class="clearfix"></div>
+<div class="tab-content">
+<div role="tabpanel" class="tab-pane active" id="figures">
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 1</strong><br>Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.</div>
+<div class="col-md-8">
+<strong>Figure 1</strong><br>Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 2</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 2</strong><br>a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 3</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 3</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 4</strong><br>a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 4</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf5"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 5</strong><br>a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 5</strong><br>a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf6"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 6</strong><br>Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 6</strong><br>Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf7"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 7</strong><br>Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 7</strong><br>Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf8"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 8</strong><br>Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 8</strong><br>Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf9"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 9</strong><br>Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 9</strong><br>Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf10"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 10</strong><br>Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 10</strong><br>Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf11"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 11</strong><br>Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 11</strong><br>Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf12"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 12</strong><br>Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.</div>
+<div class="col-md-8">
+<strong>Figure 12</strong><br>Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf13"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 13</strong><br>Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 13</strong><br>Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf14"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 14</strong><br>Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 14</strong><br>Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+</div>
+<div role="tabpanel" class="tab-pane " id="tables">
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 1</strong></strong><br> Classificação Sucessional adotada por alguns autores ao longo dos anos.</div>
+<div class="col-md-8">
+<strong><strong>Table 1</strong></strong><br> Sucessional classification adopted by some authors over the years.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 2</strong></strong><br> Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.</div>
+<div class="col-md-8">
+<strong><strong>Table 2</strong></strong><br> Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 3</strong></strong><br> Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong><strong>Table 3</strong></strong><br> Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 4</strong></strong><br> Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.</div>
+<div class="col-md-8">
+<strong><strong>Table 4</strong></strong><br> List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.</div>
+</div>
+</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf01.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 1   Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.<br>Figure 1   Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf01.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf01.jpg"></a></div>
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+<div class="modal fade ModalFigs" id="ModalFigf2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf02.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 2   a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 2   a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf02.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf02.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf03.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 3   a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 3   a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf03.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf03.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf04.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 4   a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 4   a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf04.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf04.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf5" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf05.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 5   a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>Figure 5   a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf05.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf05.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf6" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf06.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 6   Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 6   Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf06.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf06.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf7" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf07.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 7   Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 7   Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf07.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf07.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf8" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf08.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 8   Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 8   Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf08.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf08.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf9" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf09.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 9   Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 9   Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf09.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf09.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf10" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf10.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 10   Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 10   Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf10.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf10.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf11" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf11.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 11   Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 11   Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf11.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf11.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf12" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf12.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 12   Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.<br>Figure 12   Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf12.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf12.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf13" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf13.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 13   Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 13   Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf13.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf13.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf14" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf14.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 14   Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 14   Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf14.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf14.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 1</strong>    Classificação Sucessional adotada por alguns autores ao longo dos anos.<br><strong>Table 1</strong>    Sucessional classification adopted by some authors over the years.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th valign="top" align="left">Ano</th>
+<th valign="top" align="center">Autor</th>
+<th valign="top" align="center">Classificação</th>
+</tr></thead>
+<tbody>
+<tr>
+<td valign="top" align="left">1965</td>
+<td valign="top" align="center">Budowski</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">1971</td>
+<td valign="top" align="center">Gómez-Pompa</td>
+<td valign="top" align="center">Primária e secundária</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1980</sup><span class="refCtt closed"><span>Denslow, J.S. 1980. Gap partitioning among tropical rainforest trees. Biotropica 12: 47-51.</span></span></span></td>
+<td valign="top" align="center">Denslow</td>
+<td valign="top" align="center">Pioneira, secundária e sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left">1989</td>
+<td valign="top" align="center">Whitmore</td>
+<td valign="top" align="center">Pioneira e Clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">1989</td>
+<td valign="top" align="center">Kageyama &amp; Castro</td>
+<td valign="top" align="center">Pioneira, clímax e sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left">1991</td>
+<td valign="top" align="center">Gandolfi</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">1992</td>
+<td valign="top" align="center">Rodrigues &amp; Shepherd</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e típica de sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1994</sup><span class="refCtt closed"><span>Tabarelli, M. 1994. Clareiras naturais e a dinâmica sucessional de um trecho de floresta na Serra da Cantareira, SP. Dissertação Mestrado, Universidade de São Paulo, São Paulo.</span></span></span></td>
+<td valign="top" align="center">Tabarelli</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1996</sup><span class="refCtt closed"><span>Bernacci, L.C. &amp; Leitão Filho, H.F. 1996. Flora fanerogâmica da floresta da Fazenda São Vicente, Campinas, SP. Revista Brasileira de Botânica, 19: 149-164.</span></span></span></td>
+<td valign="top" align="center">Bernacci &amp; Leitão-Filho</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1997</sup><span class="refCtt closed"><span>Aragaki, S. 1997. Florística e estrutura de trecho remanescente de floresta no Planalto Paulistano (SP). São Paulo: Dissertação de Mestrado, Universidade de São Paulo, São Paulo.</span></span></span></td>
+<td valign="top" align="center">Aragaki</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">2001</td>
+<td valign="top" align="center">Aguiar <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">2006</td>
+<td valign="top" align="center">Catharino <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">2007</sup><span class="refCtt closed"><span>Polisel, R.T. &amp; Franco, G.A.D.C. 2007. Caracterização sucessional de uma floresta secundária com 40 anos de idade em Juquitiba, SP. Revista Brasileira de Biociências 5(supl. 2): 387-389.</span></span></span></td>
+<td valign="top" align="center">Polisel &amp; Franco</td>
+<td valign="top" align="center">Pioneira, secundária, tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left">2011</td>
+<td valign="top" align="center">Lima <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira e não-pioneira</td>
+</tr>
+<tr>
+<td valign="top" align="left">2011</td>
+<td valign="top" align="center">Arzolla</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left">2013</td>
+<td valign="top" align="center">Barretto</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">2017</td>
+<td valign="top" align="center">Moura &amp; Mantovani</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e sub-bosque</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 2</strong>    Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.<br><strong>Table 2</strong>    Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th align="left">Família/Espécie</th>
+<th align="center">Nome Popular</th>
+<th align="center">Área A</th>
+<th align="center">Área B</th>
+<th align="center">Área C</th>
+<th align="center">Class. Sucess.</th>
+<th align="center">Class. Sucess. (P-NP)</th>
+<th align="center">Síndrome dispersão</th>
+<th align="center">Nº de coleta</th>
+</tr></thead>
+<tbody>
+<tr>
+<td align="left">Anacardiaceae <i>Schinus terebinthifolia</i> Raddi</td>
+<td align="center">aroeira-pimenteira</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">103</td>
+</tr>
+<tr>
+<td align="left">Annonaceae <i>Annona dolabripetala</i> Raddi</td>
+<td align="center">araticum</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">117</td>
+</tr>
+<tr>
+<td align="left">
+<i>Annona emarginata</i> (Schltdl.) H.Rainer</td>
+<td align="center">araticum-mirim</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">55</td>
+</tr>
+<tr>
+<td align="left">
+<i>Annona sylvatica</i> A.St.-Hil.</td>
+<td align="center">araticum-do-mato</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">59</td>
+</tr>
+<tr>
+<td align="left">Apocynaceae <i>Aspidosperma olivaceum</i> Müll.Arg.</td>
+<td align="center">guatambu</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">61</td>
+</tr>
+<tr>
+<td align="left">Arecaceae <i>Geonoma schottiana</i> Mart.</td>
+<td align="center">guaricanga</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">74</td>
+</tr>
+<tr>
+<td align="left">
+<i>Syagrus romanzoffiana</i> (Cham.) Glassman</td>
+<td align="center">jerivá</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">88</td>
+</tr>
+<tr>
+<td align="left">Asteraceae <i>Piptocarpha macropoda</i> (DC.) Baker</td>
+<td align="center">vassourão</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">97</td>
+</tr>
+<tr>
+<td align="left">Bignoniaceae <i>Jacaranda macrantha</i> Cham.</td>
+<td align="center">carobinha</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">118</td>
+</tr>
+<tr>
+<td align="left">Boraginaceae <i>Cordia sellowiana</i> Cham.</td>
+<td align="center">louro-mole</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">47</td>
+</tr>
+<tr>
+<td align="left">Burseraceae <i>Protium heptaphyllum</i> (Aubl.) Marchand</td>
+<td align="center">almecegueira</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">130</td>
+</tr>
+<tr>
+<td align="left">Cardiopteridaceae <i>Citronella paniculata</i> (Mart.) R.A.Howard</td>
+<td align="center">congonha</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">127</td>
+</tr>
+<tr>
+<td align="left">Caricaceae <i>Jacaratia heptaphylla </i>(Vell.) A.DC.</td>
+<td align="center">jaracatiá</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">106</td>
+</tr>
+<tr>
+<td align="left">Chrysobalanaceae <i>Hirtella hebeclada</i> Moric. ex DC.</td>
+<td align="center">vermelhão</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">58</td>
+</tr>
+<tr>
+<td align="left">Clusiaceae <i>Tovomitopsis paniculata</i> (Spreng.) Planch. &amp; Triana</td>
+<td align="center">azedinho</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">63</td>
+</tr>
+<tr>
+<td align="left">Cyatheaceae <i>Alsophila setosa</i> Kaulf.</td>
+<td align="center">samambaiaçu</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">57</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cyathea delgadii </i>Sternb.</td>
+<td align="center">samambaiaçu</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">123</td>
+</tr>
+<tr>
+<td align="left">Elaeocarpaceae <i>Sloanea guianensis</i> (Aubl.) Benth.</td>
+<td align="center">sapopemba</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">129</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sloanea hirsuta</i> (Schott) Planch. ex Benth.</td>
+<td align="center">ouriço-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">18</td>
+</tr>
+<tr>
+<td align="left">Euphorbiaceae <i>Alchornea triplinervia</i> (Spreng.) Müll.Arg.</td>
+<td align="center">tapiá-mirim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">13</td>
+</tr>
+<tr>
+<td align="left">
+<i>Croton floribundus</i> Spreng.</td>
+<td align="center">capixingui</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">93</td>
+</tr>
+<tr>
+<td align="left">
+<i>Croton macrobothrys</i> Baill.</td>
+<td align="center">sangra d´água</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">60</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sapium glandulosum</i> (L.) Morong</td>
+<td align="center">leiteiro</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">124</td>
+</tr>
+<tr>
+<td align="left">Fabaceae <i>Senegalia polyphylla</i> (DC.) Britton &amp; Rose</td>
+<td align="center">monjoleiro</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">108</td>
+</tr>
+<tr>
+<td align="left">
+<i>Bauhinia forficata</i> Link</td>
+<td align="center">pata-de-vaca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">95</td>
+</tr>
+<tr>
+<td align="left">
+<i>Copaifera trapezifolia</i> Hayne</td>
+<td align="center">copaiba-da-serra</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">121</td>
+</tr>
+<tr>
+<td align="left">
+<i>Dahlstedtia pinnata</i> (Benth.) Malme</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">AUT</td>
+<td align="center">92</td>
+</tr>
+<tr>
+<td align="left">
+<i>Inga sessilis</i> (Vell.) Mart.</td>
+<td align="center">ingá-ferradura</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">113</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mimosa scabrella</i> Benth.</td>
+<td align="center">bracatinga</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">05</td>
+</tr>
+<tr>
+<td align="left">
+<i>Piptadenia gonoacantha</i> (Mart.) J.F.Macbr.</td>
+<td align="center">pau-jacaré</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">102</td>
+</tr>
+<tr>
+<td align="left">
+<i>Platymiscium floribundum</i> Vogel</td>
+<td align="center">sacambú</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">53</td>
+</tr>
+<tr>
+<td align="left">Lauraceae <i>Cinnamomum hirsutum</i> (Lorea-Hern.) Van der Werff</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">125</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cinnamomum pseudoglaziovii</i> (Lorea-Hern.) Van der Werff</td>
+<td align="center">canela-garuva</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">23</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cryptocarya mandioccana</i> Meisn.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">56</td>
+</tr>
+<tr>
+<td align="left">
+<i>Endlicheria paniculata</i> (Spreng.) J.F.Macbr.</td>
+<td align="center">canela-cheirosa</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">04</td>
+</tr>
+<tr>
+<td align="left">
+<i>Nectandra membranacea</i> (Sw.) Griseb.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">107</td>
+</tr>
+<tr>
+<td align="left">
+<i>Nectandra oppositifolia</i> Nees</td>
+<td align="center">canela-ferrugem</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">33</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea glaziovii</i> Mez</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">132</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea catharinensis</i> Mez</td>
+<td align="center">canela-preta</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">52</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea koscinskii</i> Baitello &amp; Brotto</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">70</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea</i> aff. <i>montana</i> (Meisn.) Mez</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="left"></td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea puberula</i> (Rich.) Nees</td>
+<td align="center">canela-mole</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">105</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea silvestris</i> Váttimo-Gil</td>
+<td align="center">canela-branca</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">86</td>
+</tr>
+<tr>
+<td align="left">Lecythidaceae <i>Cariniana estrellensis</i> (Raddi) Kuntze</td>
+<td align="center">jequitibá-branco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">82</td>
+</tr>
+<tr>
+<td align="left">Melastomataceae <i>Miconia budlejoides</i>Triana.</td>
+<td align="center">pixiririca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">116</td>
+</tr>
+<tr>
+<td align="left">
+<i>Miconia cinnamomifolia</i> (DC.) Naudin</td>
+<td align="center">jacatirão</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">11</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mouriri chamissoana</i> Cogn.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">31</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pleroma granulosum</i> (Desr.) D. Don</td>
+<td align="center">quaresmeira</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">101</td>
+</tr>
+<tr>
+<td align="left">Meliaceae <i>Cabralea canjerana</i> (Vell.) Mart.</td>
+<td align="center">canjerana</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">32</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cedrela fissilis</i> Vell.</td>
+<td align="center">cedro rosa</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">89</td>
+</tr>
+<tr>
+<td align="left">
+<i>Guarea macrophylla</i> Vahl ssp. <i>tuberculata</i> (Vell.) T.D.Penn.</td>
+<td align="center">marinheiro</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">24</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia pallens</i> C.DC.</td>
+<td align="center">catiguá</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">79</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia silvatica</i> C.DC.</td>
+<td align="center">catiguá</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">16</td>
+</tr>
+<tr>
+<td align="left">Monimiaceae <i>Mollinedia elegans</i> Tul.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">48</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia schottiana</i> (Spreng.) Perkins</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">01</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia triflora</i> (Spreng.) Tul.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">131</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia uleana</i> Perkins</td>
+<td align="center">capixim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">64</td>
+</tr>
+<tr>
+<td align="left">Moraceae <i>Ficus luschnathiana</i> (Miq.) Miq.</td>
+<td align="center">figueira-branca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">03</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sorocea bonplandii</i> (Baill.) W.C.Burger et al.</td>
+<td align="center">canxim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">51</td>
+</tr>
+<tr>
+<td align="left">Myristicaceae <i>Virola bicuhyba</i> (Schott ex Spreng.) Warb.</td>
+<td align="center">bicuíba</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">12</td>
+</tr>
+<tr>
+<td align="left">Myrtaceae <i>Eugenia beaurepaireana</i> (Kiaersk.) D.Legrand</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">90</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia cerasiflora</i> Miq.</td>
+<td align="center">guamirim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">38</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia cereja</i> D.Legrand</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">62</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia involucrata</i> DC.</td>
+<td align="center">cereja-do-rio-grande</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">68</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia prasina</i> O.Berg</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">20</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia subterminalis</i> DC.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">19</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia supraaxillaris</i> Spring</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">77</td>
+</tr>
+<tr>
+<td align="left">
+<i>Marlierea racemosa</i> (Vell.) Kiaersk.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">65</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia anacardiifolia</i> Gardner</td>
+<td align="center">marmelinho</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">45</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia hebepetala</i> DC.</td>
+<td align="center">guamirim</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">119</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia neobrasiliensis</i> A.R.Lourenço &amp; E.Lucas</td>
+<td align="center">araçarana</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">49</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia neolucida</i> A.R.Lourenço &amp; E.Lucas</td>
+<td align="center">araçarana</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">28</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia splendens</i> (Sw.) DC.</td>
+<td align="center">guamirim</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">54</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tenuivenosa</i> Kiaersk.</td>
+<td align="center">cambuí</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">91</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tijucensis</i> Kiaersk.</td>
+<td align="center">guamirim-ferro</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">84</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tomentosa</i> (Aubl.) DC.</td>
+<td align="center">goiaba-brava</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">39</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia</i> sp.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">54</td>
+</tr>
+<tr>
+<td align="left">Nyctaginaceae <i>Guapira opposita</i> (Vell.) Reitz</td>
+<td align="center">maria-mole</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">08</td>
+</tr>
+<tr>
+<td align="left">Olacaceae <i>Heisteria silvianii</i> Schwacke</td>
+<td align="center">brinco-de-mulata</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">14</td>
+</tr>
+<tr>
+<td align="left">Oleaceae <i>Chionanthus filiformis</i> (Vell.) P.S.Green</td>
+<td align="center">azeitona-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">35</td>
+</tr>
+<tr>
+<td align="left">Peraceae <i>Pera glabrata</i> (Schott) Baill.</td>
+<td align="center">cabeluda-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">120</td>
+</tr>
+<tr>
+<td align="left">Phyllantaceae <i>Hyeronima alchorneoides</i> Allemão</td>
+<td align="center">urucuruna</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">100</td>
+</tr>
+<tr>
+<td align="left">Phytolaccaceae <i>Seguieria langsdorffii</i> Moq.</td>
+<td align="center">limoeiro-do-mato</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">112</td>
+</tr>
+<tr>
+<td align="left">Picramniaceae <i>Picramnia glazioviana</i> Engl.</td>
+<td align="center">cafezinho</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">30</td>
+</tr>
+<tr>
+<td align="left">Polygonaceae <i>Ruprechtia laxiflora</i> Meisn.</td>
+<td align="center">marmeleiro-do-mato</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">115</td>
+</tr>
+<tr>
+<td align="left">Primulaceae <i>Myrsine gardneriana</i> A.DC.</td>
+<td align="center">capororoca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">109</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrsine umbellata</i> Mart.</td>
+<td align="center">capororoca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">110</td>
+</tr>
+<tr>
+<td align="left">Proteaceae <i>Euplassa cantareirae</i> Sleumer</td>
+<td align="center">carvalho-da-cantareira</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">50</td>
+</tr>
+<tr>
+<td align="left">Rosaceae <i>Prunus myrtifolia</i> (L.) Urb.</td>
+<td align="center">pessegueiro-bravo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">17</td>
+</tr>
+<tr>
+<td align="left">Rubiaceae <i>Cordiera myrciifolia</i> (K.Schum.) CHPerss &amp; Delprete</td>
+<td align="center">marmelinho</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">87</td>
+</tr>
+<tr>
+<td align="left">
+<i>Posoqueria latifolia</i> (Rudge) Schult.</td>
+<td align="center">baga-de-macaco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">66</td>
+</tr>
+<tr>
+<td align="left">
+<i>Psychotria suterella</i> Müll.Arg.</td>
+<td align="center">pasto-d’anta</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">22</td>
+</tr>
+<tr>
+<td align="left">
+<i>Psychotria vellosiana</i> Benth.</td>
+<td align="center">erva-de-rato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">46</td>
+</tr>
+<tr>
+<td align="left">
+<i>Rudgea gardenioides</i> (Cham.) Müll.Arg.</td>
+<td align="center">jasmim-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">122</td>
+</tr>
+<tr>
+<td align="left">Rutaceae <i>Esenbeckia grandiflora</i> Mart.</td>
+<td align="center">pau-de-cutia</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">AUT</td>
+<td align="center">67</td>
+</tr>
+<tr>
+<td align="left">Salicaceae <i>Casearia decandra</i> Jacq.</td>
+<td align="center">guaçatonga</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">83</td>
+</tr>
+<tr>
+<td align="left">
+<i>Casearia obliqua</i> Spreng.</td>
+<td align="center">guaçatonga</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">69</td>
+</tr>
+<tr>
+<td align="left">
+<i>Casearia sylvestris</i> Sw.</td>
+<td align="center">erva de lagarto</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">94</td>
+</tr>
+<tr>
+<td align="left">Sapindaceae <i>Allophylus petiolulatus</i> Radlk.</td>
+<td align="center">fruta-de-pombo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">73</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cupania oblongifolia</i> Mart.</td>
+<td align="center">cuvantã</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">09</td>
+</tr>
+<tr>
+<td align="left">
+<i>Matayba elaeagnoides</i> Radlk.</td>
+<td align="center">camboatá-branco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">76</td>
+</tr>
+<tr>
+<td align="left">
+<i>Matayba guianensis</i> Aubl.</td>
+<td align="center">camboatá-branco</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">85</td>
+</tr>
+<tr>
+<td align="left">Sapotaceae <i>Chrysophyllum inornatum</i> Mart.</td>
+<td align="center">aleixo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">75</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ecclinusa ramiflora</i> Mart.</td>
+<td align="center">guacá</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">111</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pouteria bullata</i> (S.Moore) Baehni</td>
+<td align="center">guapeva</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">114</td>
+</tr>
+<tr>
+<td align="left">Solanaceae <i>Cestrum schlechtendalii</i>. G.Don.</td>
+<td align="center">coerana</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">126</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sessea brasiliensis</i> Toledo</td>
+<td align="center">peroba-d’água</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">98</td>
+</tr>
+<tr>
+<td align="left">
+<i>Solanum pseudoquina</i> A.St.-Hil.</td>
+<td align="center">quina-falsa</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">128</td>
+</tr>
+<tr>
+<td align="left">Symplocaceae <i>Symplocos variabilis</i> Mart. ex Miq.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">71</td>
+</tr>
+<tr>
+<td align="left">Thymelaeaceae <i>Daphnopsis fasciculata</i> (Meisn.) Nevling</td>
+<td align="center">embira-branca</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">82</td>
+</tr>
+<tr>
+<td align="left">Urticaceae <i>Urera baccifera</i> (L.) Gaudich. ex Wedd.</td>
+<td align="center">urtiga</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">96</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cecropia glaziovii</i> Snethl.</td>
+<td align="center">embaúba-vermelha</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">104</td>
+</tr>
+<tr>
+<td align="left">
+<i>Coussapoa microcarpa</i> (Schott) Rizzini</td>
+<td align="center">mata-pau</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">10</td>
+</tr>
+<tr>
+<td align="left">Vochysiaceae <i>Vochysia magnifica</i> Warm.</td>
+<td align="center">guaricica</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">07</td>
+</tr>
+<tr>
+<td align="left">
+<i>Vochysia selloi</i> Warm.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">78</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 3</strong>    Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Table 3</strong>    Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th valign="bottom" align="left">Parâmetros</th>
+<th align="center">Valores Totais</th>
+<th align="center">Área A</th>
+<th align="center">Área B</th>
+<th align="center">Área C</th>
+</tr></thead>
+<tbody>
+<tr>
+<td valign="bottom" align="left">Nº de indivíduos</td>
+<td align="center">1020</td>
+<td align="center">321</td>
+<td align="center">399</td>
+<td align="center">300</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Nº de espécies</td>
+<td align="center">115</td>
+<td align="center">54</td>
+<td align="center">68</td>
+<td align="center">56</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Nº de famílias</td>
+<td align="center">45</td>
+<td align="center">26</td>
+<td align="center">32</td>
+<td align="center">30</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Densidade (ind./ha)</td>
+<td align="center">1700</td>
+<td align="center">1605</td>
+<td align="center">1995</td>
+<td align="center">1500</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Área basal total (m<sup>2</sup>)</td>
+<td align="center">23,88</td>
+<td align="center">9,079</td>
+<td align="center">8,677</td>
+<td align="center">6,124</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Dominância (m<sup>2</sup>/ha)</td>
+<td align="center">39,801</td>
+<td align="center">45,396</td>
+<td align="center">43,385</td>
+<td align="center">30,622</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Indice Shannon-Wiener</td>
+<td align="center">3,82</td>
+<td align="center">3,27</td>
+<td align="center">3,55</td>
+<td align="center">3,42</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Equabilidade</td>
+<td align="center">0,805</td>
+<td align="center">0,797</td>
+<td align="center">0,84</td>
+<td align="center">0,82</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 4</strong>    Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.<br><strong>Table 4</strong>    List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead>
+<tr>
+<th rowspan="2" align="left">Espécie</th>
+<th align="left"></th>
+<th align="center">Listas</th>
+<th align="left"></th>
+</tr>
+<tr>
+<th align="center">São Paulo</th>
+<th align="center">Brasil</th>
+<th align="center">IUCN</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">
+<i>Ocotea catharinensis</i> Mez</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cedrela fissilis</i> Vell.</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+<td align="center">EN</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia silvatica</i> C.DC.</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Virola bicuhyba</i> (Schott ex Spreng.) Warb.</td>
+<td align="center">EN</td>
+<td align="center">EN</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia prasina</i> O.Berg</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Euplassa cantareirae</i> Sleumer</td>
+<td align="center">EX</td>
+<td align="center">EN</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pouteria bullata</i> (S.Moore) Baehni</td>
+<td align="center">EN</td>
+<td align="center">EN</td>
+<td align="center">VU</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalDefault" id="ModalArticles" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Como citar</h4>
+</div>
+<div class="modal-body">
+<p id="citation"></p>
+<input id="citationCut" type="text" value=""><a class="copyLink" data-clipboard-target="#citationCut"><span class="glyphBtn copyIcon"></span>copiar</a>
+</div>
+</div></div></div>
+<script type="text/javascript">
+            function currentDate() {
+            var today = new Date();
+            var months = ['Janeiro', 'Fevereiro', 'Março', 'Abril', 'Maio', 'Junho', 'Julho', 'Agosto', 'Setembro', 'Outubro', 'Novembro', 'Dezembro']
+            today.setTime(today.getTime());
+            return today.getDate() + " " + months[today.getMonth()] + " " + today.getFullYear();
+            }
+            var citation = 'Silva, Rafaela Dias Valeck da, Cordeiro, Inês e Arzolla, Frederico Alexandre Roccia Dal PozzoFlorestas secundárias do Parque Estadual da Cantareira, São Paulo, SP, Brasil: Variações florísticas e estruturais11Parte da Dissertação de Mestrado do primeiro Autor. Hoehnea [online]. 2022, v. 49 [Acessado CURRENTDATE] , e1082020. Disponível em: &lt;https://doi.org/10.1590/2236-8906-108/2020&gt;. Epub 24 Jan 2022. ISSN 2236-8906. https://doi.org/10.1590/2236-8906-108/2020.'.replace('CURRENTDATE', currentDate());
+            document.getElementById('citation').innerHTML = citation;
+            document.getElementById('citationCut').value = citation.replace('&lt;', '<').replace('&gt;', ">");
+        </script>
+</div>
+<ul class="floatingMenu fm-slidein" data-fm-toogle="hover"><li class="fm-wrap">
+<a href="javascript:;" class="fm-button-main"><span class="sci-ico-floatingMenuDefault glyphFloatMenu"></span><span class="sci-ico-floatingMenuClose glyphFloatMenu"></span></a><ul class="fm-list">
+<li><a class="fm-button-child" data-fm-label="Figuras | Tabelas" data-toggle="modal" data-target="#ModalTablesFigures"><span class="sci-ico-figures glyphFloatMenu"></span></a></li>
+<li><a class="fm-button-child" data-toggle="modal" data-target="#ModalArticles" data-fm-label="How to
+                                          cite"><span class="sci-ico-citation glyphFloatMenu"></span></a></li>
+</ul>
+</li></ul>
+<script src="/Users/roberta.takenaka/github.com/scieloorg/packtools/packtools/catalogs/htmlgenerator/static/scielo-article-standalone-min.js"></script>
+</body>
+</html>
diff --git a/tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/2236-8906-hoehnea-49-e1082020.xml b/tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/2236-8906-hoehnea-49-e1082020.xml
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@@ -0,0 +1,2890 @@
+<?xml version="1.0" encoding="UTF-8"?>
+<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Publishing DTD v1.1 20151215//EN" "https://jats.nlm.nih.gov/publishing/1.1/JATS-journalpublishing1.dtd">
+<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" article-type="research-article" dtd-version="1.1" specific-use="sps-1.9" xml:lang="pt">
+    <front>
+        <journal-meta>
+            <journal-id journal-id-type="publisher-id">Hoehnea</journal-id>
+            <journal-title-group>
+                <journal-title>Hoehnea</journal-title>
+                <abbrev-journal-title abbrev-type="publisher">Hoehnea</abbrev-journal-title>
+            </journal-title-group>
+            <issn pub-type="epub">2236-8906</issn>
+            <issn pub-type="ppub">0073-2877</issn>
+            <publisher>
+                <publisher-name>Instituto de Pesquisas Ambientais</publisher-name>
+            </publisher>
+        </journal-meta>
+        <article-meta>
+            <article-id pub-id-type="doi">10.1590/2236-8906-108/2020</article-id>
+            <article-id pub-id-type="other">00206</article-id>
+            <article-categories>
+                <subj-group subj-group-type="heading">
+                    <subject>Artigo</subject>
+                </subj-group>
+            </article-categories>
+            <title-group>
+                <article-title>Florestas secund&#x00E1;rias do Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil: Varia&#x00E7;&#x00F5;es flor&#x00ED;sticas e estruturais<sup><xref ref-type="fn" rid="fn1">1</xref></sup></article-title>
+                <trans-title-group xml:lang="en">
+                    <trans-title>Secondary forests of the Parque Estadual da Cantareira, S&#x00E3;o Paulo State, SP, Brasil: Floristic and structural variations</trans-title>
+                </trans-title-group>
+            </title-group>
+            <contrib-group>
+                <contrib contrib-type="author">
+                    <contrib-id contrib-id-type="orcid">0000-0002-9049-3704</contrib-id>
+                    <name>
+                        <surname>Silva</surname>
+                        <given-names>Rafaela Dias Valeck da</given-names>
+                    </name>
+                    <xref ref-type="aff" rid="aff2">2</xref>
+                    <xref ref-type="corresp" rid="c1">4</xref>
+                </contrib>
+                <contrib contrib-type="author">
+                    <contrib-id contrib-id-type="orcid">0000-0002-2626-5280</contrib-id>
+                    <name>
+                        <surname>Cordeiro</surname>
+                        <given-names>In&#x00EA;s</given-names>
+                    </name>
+                    <xref ref-type="aff" rid="aff2">2</xref>
+                </contrib>
+                <contrib contrib-type="author">
+                    <contrib-id contrib-id-type="orcid">0000-0003-3111-6877</contrib-id>
+                    <name>
+                        <surname>Arzolla</surname>
+                        <given-names>Frederico Alexandre Roccia Dal Pozzo</given-names>
+                    </name>
+                    <xref ref-type="aff" rid="aff3">3</xref>
+                </contrib>
+            </contrib-group>
+            <aff id="aff2"><label>2</label>
+                <institution content-type="orgname">Instituto de Bot&#x00E2;nica</institution>
+                <addr-line>
+                    <postal-code>04301-902</postal-code>
+                    <city>S&#x00E3;o Paulo</city>
+                    <state>SP</state>
+                </addr-line>
+                <country country="BR">Brasil</country>
+                <institution content-type="original">Instituto de Bot&#x00E2;nica, Avenida Miguel Estefano, 3.687, 04301-902 S&#x00E3;o Paulo, SP, Brasil</institution></aff>
+            <aff id="aff3"><label>3</label>
+                <institution content-type="orgname">Instituto Florestal</institution>
+                <addr-line>
+                    <postal-code>02377-000</postal-code>
+                    <city>S&#x00E3;o Paulo</city>
+                    <state>SP</state>
+                </addr-line>
+                <country country="BR">Brasil</country>
+                <institution content-type="original">Instituto Florestal, Rua do Horto, 931, 02377-000 S&#x00E3;o Paulo, SP, Brasil</institution></aff>
+            <author-notes>
+                <fn fn-type="edited-by">
+                    <p>Editora Associada: Cl&#x00E1;udia Baider</p>
+                </fn>
+                <fn id="fn1" fn-type="other">
+                    <label>1</label>
+                    <p>Parte da Disserta&#x00E7;&#x00E3;o de Mestrado do primeiro Autor</p>
+                </fn>
+                <corresp id="c1"><label>4</label> Autora para correspond&#x00EA;ncia: <email>rafaela_valeck@hotmail.com</email></corresp>
+            </author-notes>
+            <pub-date publication-format="electronic" date-type="pub">
+                <day>24</day>
+                <month>01</month>
+                <year>2022</year>
+            </pub-date>
+            <pub-date date-type="collection" publication-format="electronic">
+                <year>2022</year>
+            </pub-date>
+            <volume>49</volume>
+            <elocation-id>e1082020</elocation-id>
+            <history>
+                <date date-type="received">
+                    <day>13</day>
+                    <month>10</month>
+                    <year>2020</year>
+                </date>
+                <date date-type="accepted">
+                    <day>03</day>
+                    <month>11</month>
+                    <year>2021</year>
+                </date>
+            </history>
+            <permissions>
+                <license license-type="open-access" xlink:href="http://creativecommons.org/licenses/by/4.0/" xml:lang="pt">
+                    <license-p>Este &#x00E9; um artigo publicado em acesso aberto (Open Access) sob a licen&#x00E7;a Creative Commons Attribution, que permite uso, distribui&#x00E7;&#x00E3;o e reprodu&#x00E7;&#x00E3;o em qualquer meio, sem restri&#x00E7;&#x00F5;es desde que o trabalho original seja corretamente citado.</license-p>
+                </license>
+            </permissions>
+            <abstract>
+                <title>RESUMO</title>
+                <p>O Parque Estadual da Cantareira, no bioma da Mata Atl&#x00E2;ntica, foi criado a partir da desapropria&#x00E7;&#x00E3;o de fazendas de caf&#x00E9; para prote&#x00E7;&#x00E3;o de mananciais para a cidade de S&#x00E3;o Paulo em 1877. Desde ent&#x00E3;o, poucas atividades humanas ocorreram em seu interior. Aqui, comparamos a composi&#x00E7;&#x00E3;o e o est&#x00E1;gio sucessional de diferentes fragmentos de floresta pr&#x00F3;ximos (&#x003C;0,5 km um do outro). Foram levantados 0,6 ha, divididos em tr&#x00EA;s &#x00E1;reas de 0,2 ha cada, com &#x00E1;rvores atingindo PAP &#x2265; 15 cm, sendo amostradas, identificadas e medidos o di&#x00E2;metro e a altura. O est&#x00E1;gio sucessional das esp&#x00E9;cies foi determinado e um perfil de cada &#x00E1;rea foi desenhado em escala. Um total de 1.020 indiv&#x00ED;duos pertencentes a 45 fam&#x00ED;lias e 115 esp&#x00E9;cies foi amostrado. Os fragmentos variaram em n&#x00FA;mero de indiv&#x00ED;duos (300-399 indiv&#x00ED;duos), fam&#x00ED;lias (N = 26-32) e esp&#x00E9;cies (N = 54-68), altura e est&#x00E1;gios sucessionais, indicando alta heterogeneidade dentro de uma floresta cont&#x00ED;nua, desde os est&#x00E1;gios sucessionais maduros at&#x00E9; os iniciais. Essas descobertas t&#x00EA;m implica&#x00E7;&#x00F5;es para o manejo da conserva&#x00E7;&#x00E3;o e os servi&#x00E7;os ecossist&#x00EA;micos fornecidos por eles.</p>
+            </abstract>
+            <trans-abstract xml:lang="en">
+                <title>ABSTRACT</title>
+                <p>The Parque Estadual da Cantareira, in the Atlantic Forest biome, was created from the expropriation of coffee farms for the protection of water sources for S&#x00E3;o Paulo city in 1877. Since then, few human activities have taken place in its interior. Here, we compare the composition and the successional stages of different fragments of near forests (&#x003C;0.5 km of each other); 0.6 ha were raised, divided in three areas of 0.2 ha each, with trees reaching PAP &#x2265; 15 cm, being sampled, identified and measured for diameter and height. The succession stage of the species was determined and a profile of each area was drawn in scale. A total of 1,020 individuals of 45 families and 115 species was sampled. The fragments varies in number of in individuals (300-399 individuals), families (N = 26-32) and species (N = 54-68), height and successional stages, indicating high heterogeneity within a continuous forest, from the mature successional stages to the first ones. These discoveries have implications for conservation management and the ecosystem service they provide.</p>
+            </trans-abstract>
+            <kwd-group xml:lang="pt">
+                <title>Palavras-chave:</title>
+                <kwd>Fitossociologia</kwd>
+                <kwd>Mata Atl&#x00E2;ntica</kwd>
+                <kwd>sucess&#x00E3;o</kwd>
+            </kwd-group>
+            <kwd-group xml:lang="en">
+                <title>Keywords:</title>
+                <kwd>Atlantic Rainforest</kwd>
+                <kwd>Phytosociology</kwd>
+                <kwd>succession</kwd>
+            </kwd-group>
+        </article-meta>
+    </front>
+    <body>
+        <sec sec-type="intro">
+            <title>Introdu&#x00E7;&#x00E3;o</title>
+            <p>A Mata Atl&#x00E2;ntica ocupa aproximadamente 15% do territ&#x00F3;rio brasileiro sendo considerada mundialmente o 5&#x00BA; bioma mais amea&#x00E7;ado (<xref ref-type="bibr" rid="B23">Funda&#x00E7;&#x00E3;o SOS Mata Atl&#x00E2;ntica 2020</xref>). Estende-se desde o Piau&#x00ED; at&#x00E9; o Estado do Rio Grande do Sul, englobando assim 17 Estados brasileiros (<xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo 2010</xref>, <xref ref-type="bibr" rid="B23">Funda&#x00E7;&#x00E3;o SOS Mata Atl&#x00E2;ntica 2020</xref>). A ampla varia&#x00E7;&#x00E3;o de temperatura, relevo e solo ao longo da Mata Atl&#x00E2;ntica, fazem desta uma das florestas de maior biodiversidade do mundo (<xref ref-type="bibr" rid="B35">Leit&#x00E3;o-Filho 1987</xref>, <xref ref-type="bibr" rid="B38">Lino &#x0026; Amaral 2018</xref>). Pelo alto n&#x00FA;mero de esp&#x00E9;cies end&#x00EA;micas e forte press&#x00E3;o antr&#x00F3;pica, o Bioma Mata Atl&#x00E2;ntica, juntamente com o Cerrado, &#x00E9; considerado um dos hostspots do planeta (<xref ref-type="bibr" rid="B42">Myers <italic>et al</italic>. 2000</xref>)</p>
+            <p>A Mata Atl&#x00E2;ntica &#x00E9; composta pelas seguintes forma&#x00E7;&#x00F5;es vegetais: Floresta Ombr&#x00F3;fila Densa, Aberta e Mista (conhecida como Floresta de Arauc&#x00E1;rias); Floresta Estacional Semidecidual e Decidual; Campos de Altitude; Manguezais, Restingas, Campos Salinos e &#x00C1;reas Aluviais; &#x00C1;reas de Tens&#x00E3;o Ecol&#x00F3;gica; Ref&#x00FA;gios Vegetacionais (<xref ref-type="bibr" rid="B29">IBGE 2019</xref>, <xref ref-type="bibr" rid="B23">Funda&#x00E7;&#x00E3;o SOS Mata Atl&#x00E2;ntica 2020</xref>).</p>
+            <p>As Florestas Ombr&#x00F3;filas Densas se subdividem em 5 grupos principais: Floresta Ombr&#x00F3;fila Densa de Terras Baixas, presente at&#x00E9; 50 metros de altitude; Floresta Ombr&#x00F3;fila Densa Submontana, 50 a 500 metros; Floresta Ombr&#x00F3;fila Densa Montana, 500 a 1500 metros e a Floresta Ombr&#x00F3;fila Densa Altomontana, acima de 1500 metros, e a Floresta Ombr&#x00F3;fila Densa Aluvial, presente em qualquer das forma&#x00E7;&#x00F5;es anteriores, ao longo dos cursos d&#x2019;&#x00E1;gua (<xref ref-type="bibr" rid="B28">IBGE 2012</xref>).</p>
+            <p>No Estado de S&#x00E3;o Paulo, a diminui&#x00E7;&#x00E3;o dr&#x00E1;stica da cobertura florestal deveu-se a fatores antr&#x00F3;picos, principalmente o estabelecimento de culturas, inicialmente a do caf&#x00E9; e o adensamento populacional nos n&#x00FA;cleos urbanos (<xref ref-type="bibr" rid="B45">Rocha &#x0026; Costa 1998</xref>, RBMA 2019).</p>
+            <p>Apesar da destrui&#x00E7;&#x00E3;o da floresta ao longo da hist&#x00F3;ria de S&#x00E3;o Paulo, o Estado ainda preserva a maior &#x00E1;rea cont&#x00ED;nua da Mata Atl&#x00E2;ntica no Brasil, nas encostas da Serra do Mar (<xref ref-type="bibr" rid="B36">Leite 2007</xref>). Alguns trabalhos mais recentes relatam o aumento da cobertura florestal, representada por florestas secund&#x00E1;rias em diferentes est&#x00E1;gios de regenera&#x00E7;&#x00E3;o (<xref ref-type="bibr" rid="B21">Farinaci &#x0026; Batistella 2012</xref>).</p>
+            <p>O que resta da Mata Atl&#x00E2;ntica est&#x00E1; inserido em 1.324 Unidades de Conserva&#x00E7;&#x00E3;o (UCs). As Unidades de Conserva&#x00E7;&#x00E3;o possuem uma classifica&#x00E7;&#x00E3;o pr&#x00F3;pria, pois a diversidade do ambiente resulta em objetivos e manejos distintos.</p>
+            <p>A sucess&#x00E3;o &#x00E9; o processo natural de desenvolvimento da comunidade vegetal que possibilita o estabelecimento de plantas em uma &#x00E1;rea desprovida de vegeta&#x00E7;&#x00E3;o ou a regenera&#x00E7;&#x00E3;o da vegeta&#x00E7;&#x00E3;o onde esta sofreu algum tipo de dist&#x00FA;rbio (<xref ref-type="bibr" rid="B14">Brancalion <italic>et al.</italic> 2015</xref>).</p>
+            <p>Para cada fase da sucess&#x00E3;o, em uma floresta secund&#x00E1;ria, h&#x00E1; predom&#x00ED;nio de determinadas esp&#x00E9;cies pertencentes a um grupo sucessional (<xref ref-type="bibr" rid="B18">Clements 1916</xref>). Segundo <xref ref-type="bibr" rid="B54">Whitmore (1989)</xref>, o conhecimento sobre a substitui&#x00E7;&#x00E3;o de esp&#x00E9;cies ao longo do processo de sucess&#x00E3;o, &#x00E9; fundamental para avaliar o grau de maturidade em que se encontra um determinado fragmento florestal.</p>
+            <p>Conforme a <xref ref-type="table" rid="t1">tabela 1</xref>, o primeiro estudo a classificar as esp&#x00E9;cies por suas respectivas categorias foi realizado por <xref ref-type="bibr" rid="B16">Budowski (1965)</xref>, este utilizou as categorias pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e cl&#x00ED;max. Posteriormente, alguns autores classificaram as esp&#x00E9;cies de forma mais sucinta, ou seja, esp&#x00E9;cies pioneiras e n&#x00E3;o-pioneiras como: <xref ref-type="bibr" rid="B27">G&#x00F3;mez-Pompa (1971)</xref>, <xref ref-type="bibr" rid="B54">Whitmore (1989)</xref> e <xref ref-type="bibr" rid="B37">Lima <italic>et al</italic>. (2011)</xref>. J&#x00E1;, em outros estudos, os autores optaram por classificar as esp&#x00E9;cies separando as n&#x00E3;o pioneiras, por secund&#x00E1;rias iniciais e secund&#x00E1;rias tardias e as esp&#x00E9;cies t&#x00ED;picas de sub-bosque ou conhecidas como umbr&#x00F3;filas.</p>
+            <p>Portanto, conforme as an&#x00E1;lises dos estudos apresentados na <xref ref-type="table" rid="t1">tabela 1</xref>, as esp&#x00E9;cies pioneiras predominam no in&#x00ED;cio da sucess&#x00E3;o, podem ser encontradas em grandes clareiras, produzem sementes pequenas e abundantes, que necessitam de luz direta para germinar, al&#x00E9;m disso tem crescimento r&#x00E1;pido e ciclo de vida curto; as esp&#x00E9;cies secund&#x00E1;rias iniciais estabelecem-se em pequenas clareiras, assemelham-se &#x00E0;s pioneiras quanto &#x00E0; necessidade de luz para germinar suas sementes, mas t&#x00EA;m ciclo de vida mais longo; as secund&#x00E1;rias tardias destacam-se na fase mais madura da floresta, suas sementes n&#x00E3;o necessitam de luz direta para germinar e s&#x00E3;o geralmente maiores, menos abundantes que as das esp&#x00E9;cies pioneiras, podem apresentar dorm&#x00EA;ncia e suas pl&#x00E2;ntulas vivem na sombra, com crescimento lento e ciclo de vida longo; as esp&#x00E9;cies umbr&#x00F3;filas ou t&#x00ED;picas de sub-bosque, est&#x00E3;o presentes em todas as fases, mas com maior densidade na fase madura. O que as diferem das secund&#x00E1;rias tardias &#x00E9; que em todo seu ciclo de vida se desenvolvem inteiramente no estrato inferior da floresta (<xref ref-type="bibr" rid="B16">Budowski 1965</xref>, <xref ref-type="bibr" rid="B27">G&#x00F3;mez-Pompa 1971</xref>, <xref ref-type="bibr" rid="B51">Swaine &#x0026; Whitmore 1988</xref>, <xref ref-type="bibr" rid="B31">Kageyama &#x0026; Castro 1989</xref>, <xref ref-type="bibr" rid="B24">Gandolfi 1991</xref>, <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. 2006</xref>).</p>
+            <p>No Estado de S&#x00E3;o Paulo, uma importante unidade de conserva&#x00E7;&#x00E3;o &#x00E9; o Parque Estadual da Cantareira, localizado na regi&#x00E3;o metropolitana da cidade de S&#x00E3;o Paulo, sendo um dos principais remanescentes florestais, formados por florestas secund&#x00E1;rias em diferentes est&#x00E1;gios sucessionais, por&#x00E9;m mantendo alta riqueza de biodiversidade.</p>
+            <p>Estudos sobre a din&#x00E2;mica do processo sucessional em florestas do Planalto Paulista s&#x00E3;o escassos. Portanto, o presente estudo poder&#x00E1; fornecer contribui&#x00E7;&#x00F5;es para a tem&#x00E1;tica e para aplica&#x00E7;&#x00F5;es pr&#x00E1;ticas no &#x00E2;mbito local e regional.</p>
+            <p>O objetivo deste estudo foi comparar quanto ao est&#x00E1;gio sucessional, trechos da floresta do Parque Estadual da Cantareira atrav&#x00E9;s da an&#x00E1;lise de sua estrutura e esp&#x00E9;cies caracter&#x00ED;sticas de seus estratos, contribuindo para o conhecimento, conserva&#x00E7;&#x00E3;o e a prote&#x00E7;&#x00E3;o das florestas secund&#x00E1;rias urbanas.</p>
+            <p>Para tanto elaboramos as seguintes perguntas:</p>
+            <p>A. Como a composi&#x00E7;&#x00E3;o flor&#x00ED;stica e a estrutura variam nas &#x00E1;reas analisadas?</p>
+            <p>B. &#x00C9; poss&#x00ED;vel reconhecer est&#x00E1;gios sucessionais diferentes nas &#x00E1;reas estudadas?</p>
+            <p>C. Como as esp&#x00E9;cies de diferentes grupos sucessionais est&#x00E3;o representadas nas &#x00E1;reas estudadas?</p>
+        </sec>
+        <sec sec-type="materials|methods">
+            <title>Material e M&#x00E9;todos</title>
+            <p>&#x00C1;rea de Estudo - O Parque Estadual da Cantareira (PEC) possui 7.916,5 hectares, abrangendo parte dos mun&#x00ED;cipios de Caieiras, Guarulhos, Mairipor&#x00E3; e S&#x00E3;o Paulo, na bacia do Alto Tiet&#x00EA;, na Serra da Cantareira. Destaca-se entre seus servi&#x00E7;os ecossist&#x00EA;micos, a grande riqueza de mananciais que abriga em sua &#x00E1;rea (<xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo, 2010</xref>).</p>
+            <p>Essa regi&#x00E3;o anteriormente &#x00E9; composta por fazendas de caf&#x00E9;, que foram adquiridas pelo governo do Estado, preocupado com o abastecimento de &#x00E1;gua. A capta&#x00E7;&#x00E3;o de &#x00E1;gua na Serra da Cantareira iniciou-se em 1877. O abastecimento acontecia a partir de um sistema de pequenas represas, suficientes para abastecer a popula&#x00E7;&#x00E3;o que residia no centro da cidade com uma &#x00E1;gua de excelente qualidade. Com o aumento da urbaniza&#x00E7;&#x00E3;o, os mananciais da Serra da Cantareira deixaram de ser suficientes para o abastecimento da cidade de S&#x00E3;o Paulo. Atualmente, apenas uma parte do munic&#x00ED;pio de Guarulhos &#x00E9; abastecida pelos mananciais do PEC (<xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo, 2010</xref>).</p>
+            <p>Como resultado deste hist&#x00F3;rico, formou-se uma floresta secund&#x00E1;ria, onde predominam manchas em fases intermedi&#x00E1;rias de sucess&#x00E3;o (<xref ref-type="bibr" rid="B8">Baitello <italic>et al</italic>. 1993</xref>, <xref ref-type="bibr" rid="B5">Arzolla 2002</xref>, <xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo 2010</xref>).</p>
+            <p>O PEC &#x00E9; composto por 4 zonas administrativas: N&#x00FA;cleo Engordador, localizado entre os munic&#x00ED;pios de Mairipor&#x00E3; e S&#x00E3;o Paulo; &#x00C1;guas Claras, no munic&#x00ED;pio de Mairipor&#x00E3;; Cabu&#x00E7;u em Guarulhos e Pedra Grande, que abrange parte dos munic&#x00ED;pios de Caieiras, Mairipor&#x00E3; e S&#x00E3;o Paulo (<xref ref-type="bibr" rid="B7">Ayres 2006</xref>, <xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo 2010</xref>).</p>
+            <p>A &#x00E1;rea de estudo est&#x00E1; localizada no N&#x00FA;cleo Pedra Grande. Conforme o <xref ref-type="bibr" rid="B28">IBGE (2012)</xref>, a &#x00E1;rea &#x00E9; recoberta pela Floresta Ombr&#x00F3;fila Densa Montana. De acordo com a classifica&#x00E7;&#x00E3;o de K&#x00F6;ppen, o clima &#x00E9; do tipo &#x00FA;mido, temperado e sem esta&#x00E7;&#x00E3;o seca - Cfb (<xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo 2010</xref>), ou seja, com precipita&#x00E7;&#x00E3;o m&#x00E9;dia do m&#x00EA;s mais seco &#x003E; 30 mm e a temperatura m&#x00E9;dia do m&#x00EA;s mais quente &#x003C;22&#x00BA;C (<xref ref-type="bibr" rid="B34">K&#x00F6;ppen 2019</xref>). O relevo &#x00E9; montanhoso, com amplitudes de 120 a 400 metros e altitudes de 875 a 1215 metros (<xref ref-type="bibr" rid="B47">S&#x00E3;o Paulo, 2010</xref>).</p>
+            <table-wrap-group id="t1">
+                <table-wrap xml:lang="pt">
+                    <label>Tabela 1</label>
+                    <caption>
+                        <title>Classifica&#x00E7;&#x00E3;o Sucessional adotada por alguns autores ao longo dos anos.</title>
+                    </caption>
+                </table-wrap>
+                <table-wrap xml:lang="en">
+                    <label>Table 1</label>
+                    <caption>
+                        <title>Sucessional classification adopted by some authors over the years.</title>
+                    </caption>
+                    <table>
+                        <thead>
+                            <tr>
+                                <th valign="top" align="left">Ano</th>
+                                <th valign="top" align="center">Autor</th>
+                                <th valign="top" align="center">Classifica&#x00E7;&#x00E3;o</th>
+                            </tr>
+                        </thead>
+                        <tbody>
+                            <tr>
+                                <td valign="top" align="left">1965</td>
+                                <td valign="top" align="center">Budowski</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e cl&#x00ED;max</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">1971</td>
+                                <td valign="top" align="center">G&#x00F3;mez-Pompa</td>
+                                <td valign="top" align="center">Prim&#x00E1;ria e secund&#x00E1;ria</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left"><xref ref-type="bibr" rid="B19">1980</xref></td>
+                                <td valign="top" align="center">Denslow</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria e sub-bosque</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">1989</td>
+                                <td valign="top" align="center">Whitmore</td>
+                                <td valign="top" align="center">Pioneira e Cl&#x00ED;max</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">1989</td>
+                                <td valign="top" align="center">Kageyama &#x0026; Castro</td>
+                                <td valign="top" align="center">Pioneira, cl&#x00ED;max e sub-bosque</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">1991</td>
+                                <td valign="top" align="center">Gandolfi</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial e secund&#x00E1;ria tardia</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">1992</td>
+                                <td valign="top" align="center">Rodrigues &#x0026; Shepherd</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e t&#x00ED;pica de sub-bosque</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left"><xref ref-type="bibr" rid="B53">1994</xref></td>
+                                <td valign="top" align="center">Tabarelli</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e cl&#x00ED;max</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left"><xref ref-type="bibr" rid="B11">1996</xref></td>
+                                <td valign="top" align="center">Bernacci &#x0026; Leit&#x00E3;o-Filho</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial e secund&#x00E1;ria tardia</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left"><xref ref-type="bibr" rid="B4">1997</xref></td>
+                                <td valign="top" align="center">Aragaki</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial e secund&#x00E1;ria tardia</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2001</td>
+                                <td valign="top" align="center">Aguiar <italic>et al</italic>.</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e cl&#x00ED;max</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2006</td>
+                                <td valign="top" align="center">Catharino <italic>et al</italic>.</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e umbr&#x00F3;fila</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left"><xref ref-type="bibr" rid="B44">2007</xref></td>
+                                <td valign="top" align="center">Polisel &#x0026; Franco</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria, tardia e umbr&#x00F3;fila</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2011</td>
+                                <td valign="top" align="center">Lima <italic>et al</italic>.</td>
+                                <td valign="top" align="center">Pioneira e n&#x00E3;o-pioneira</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2011</td>
+                                <td valign="top" align="center">Arzolla</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e umbr&#x00F3;fila</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2013</td>
+                                <td valign="top" align="center">Barretto</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial e secund&#x00E1;ria tardia</td>
+                            </tr>
+                            <tr>
+                                <td valign="top" align="left">2017</td>
+                                <td valign="top" align="center">Moura &#x0026; Mantovani</td>
+                                <td valign="top" align="center">Pioneira, secund&#x00E1;ria inicial, secund&#x00E1;ria tardia e sub-bosque</td>
+                            </tr>
+                        </tbody>
+                    </table>
+                </table-wrap>
+            </table-wrap-group>
+            <p>M&#x00E9;todos - Para o presente estudo foram selecionadas tr&#x00EA;s &#x00E1;reas amostrais de 0,2 ha cada, subdivididas em dez parcelas cont&#x00ED;guas de 10 x 20 m, totalizando uma &#x00E1;rea amostral de 0,6 ha. A dist&#x00E2;ncia aproximada entre a &#x00E1;rea C e A &#x00E9; de 250 m e da &#x00E1;rea A para B de 400 m, com as respectivas localiza&#x00E7;&#x00F5;es: &#x00E1;rea A (23&#x00B0;25&#x2019;46&#x201D;S, 46&#x00B0;38&#x2019;6&#x201D;O), &#x00E1;rea B (23&#x00B0;25&#x2019;40&#x201D;S, 46&#x00B0;37&#x2019;54&#x201D;O) e &#x00E1;rea C (23&#x00B0;25&#x2019;53&#x201D;S, 46&#x00B0;38&#x2019;0&#x201D;O) (<xref ref-type="fig" rid="f1">figura 1</xref>). As tr&#x00EA;s &#x00E1;reas encontram-se afastadas das trilhas para se evitar o efeito de borda, como recomendado por <xref ref-type="bibr" rid="B46">Rodrigues &#x0026; Shepherd (1992)</xref> e possuem declividades semelhantes.</p>
+            <p>Foram amostrados todos os indiv&#x00ED;duos com PAP, per&#x00ED;metro do tronco &#x00E0; altura de 1,30 m acima do solo &#x2265; 15 cm. Os indiv&#x00ED;duos mortos, mesmo em p&#x00E9;, n&#x00E3;o foram amostrados. A altura das &#x00E1;rvores foi estimada utilizando-se tesoura de poda alta como refer&#x00EA;ncia. As amostras bot&#x00E2;nicas foram coletadas, herborizadas e identificadas por compara&#x00E7;&#x00E3;o com exsicatas depositadas em herb&#x00E1;rio, consultas a especialistas e bibliografias espec&#x00ED;ficas. As amostras f&#x00E9;rteis foram registradas e incorporadas no Herb&#x00E1;rio Dom Bento Pickel (SPSF) do Instituto Florestal.</p>
+            <p>Para a classifica&#x00E7;&#x00E3;o das fam&#x00ED;lias, foi utilizado o Angiosperm Phylogeny Group - APG IV (<xref ref-type="bibr" rid="B3">APG - Angiosperm Phylogeny Group 2016</xref>). Os nomes cient&#x00ED;ficos foram conferidos com a lista de esp&#x00E9;cies da Flora do Brasil (<xref ref-type="bibr" rid="B22">Flora do Brasil 2020 - em constru&#x00E7;&#x00E3;o 2020</xref>).</p>
+            <p>Os par&#x00E2;metros fitossociol&#x00F3;gicos calculados nas an&#x00E1;lises foram: n&#x00FA;mero de indiv&#x00ED;duos (ni), densidade relativa (DR), domin&#x00E2;ncia relativa (DoR), frequ&#x00EA;ncia relativa (FR), valor de cobertura (VC) e valor de import&#x00E2;ncia (VI), segundo <xref ref-type="bibr" rid="B41">Mueller-Dombois &#x0026; Ellenberg (1974)</xref>. Tamb&#x00E9;m foram realizadas an&#x00E1;lises multivariadas de classifica&#x00E7;&#x00E3;o e ordena&#x00E7;&#x00E3;o, utilizando-se matrizes de n&#x00FA;mero de indiv&#x00ED;duos, para verificar a eventual forma&#x00E7;&#x00E3;o de grupos nas unidades amostrais da &#x00E1;rea de estudo e comparar as parcelas e blocos entre si. Nas an&#x00E1;lises de classifica&#x00E7;&#x00E3;o, para compara&#x00E7;&#x00E3;o de matrizes de n&#x00FA;meros de indiv&#x00ED;duos, foram utilizados os m&#x00E9;todos UPGMA - Unweighted Pair Group Method with Arithmetic Mean com coeficiente de Bray-Curtis. Como m&#x00E9;todo de ordena&#x00E7;&#x00E3;o foi utilizado CA (An&#x00E1;lise de Correspond&#x00EA;ncia). Para esses c&#x00E1;lculos e an&#x00E1;lises, foi utilizado o programa Fitopac 2.1 (<xref ref-type="bibr" rid="B49">Shepherd 2010</xref>).</p>
+            <p>As esp&#x00E9;cies foram classificadas segundo o tipo de dispers&#x00E3;o de seus prop&#x00E1;gulos, como zooc&#x00F3;ricas, anemoc&#x00F3;ricas e autoc&#x00F3;ricas, de acordo com <xref ref-type="bibr" rid="B5">Arzolla (2002</xref>, <xref ref-type="bibr" rid="B6">2011</xref>); <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref> e <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref>.</p>
+            <p>A apresenta&#x00E7;&#x00E3;o das esp&#x00E9;cies amea&#x00E7;adas deu-se pelas consultas &#x00E0;s seguintes listas: IUCN (2020), nacional (Portaria MMA n&#x00BA; 443, de 17 de dezembro de 2014 - Brasil 2020) e estadual (Resolu&#x00E7;&#x00E3;o SMA N&#x00BA; 57, de 05 de junho de 2016 - <xref ref-type="bibr" rid="B48">S&#x00E3;o Paulo 2016</xref>).</p>
+            <p>A classifica&#x00E7;&#x00E3;o das esp&#x00E9;cies, segundo a categoria sucessional, foi baseada, principalmente, em observa&#x00E7;&#x00F5;es de campo e em trabalhos realizados por <xref ref-type="bibr" rid="B6">Arzolla (2011)</xref> e <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref>. Foram feitas duas classifica&#x00E7;&#x00F5;es sucessionais, uma com quatro categorias: pioneiras, secund&#x00E1;rias iniciais, secund&#x00E1;rias tardias e umbr&#x00F3;filas, sendo as tr&#x00EA;s primeiras conforme <xref ref-type="bibr" rid="B16">Budowski (1965)</xref> e, as umbr&#x00F3;filas, segundo <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref> e <xref ref-type="bibr" rid="B6">Arzolla (2011)</xref>; a segunda considerou as esp&#x00E9;cies como pioneiras e n&#x00E3;o-pioneiras (Secund&#x00E1;rias iniciais, tardias e umbr&#x00F3;filas), adaptado de <xref ref-type="bibr" rid="B9">Barbosa (2017)</xref>.</p>
+            <p>Para auxiliar uma an&#x00E1;lise da distribui&#x00E7;&#x00E3;o das esp&#x00E9;cies em categoria sucessional, foram idealizados perfis diagramas totais de cada uma das &#x00E1;reas estudadas, com a representa&#x00E7;&#x00E3;o dos indiv&#x00ED;duos amostrados seguindo-se a sequ&#x00EA;ncia da planilha de campo, com n&#x00FA;cleos diferentes segundo sua classifica&#x00E7;&#x00E3;o sucessional.</p>
+        </sec>
+        <sec sec-type="results">
+            <title>Resultados</title>
+            <fig-group id="f1">
+                <fig xml:lang="pt">
+                    <label>Figura 1</label>
+                    <caption>
+                        <title>Mapa com a localiza&#x00E7;&#x00E3;o das tr&#x00EA;s &#x00E1;reas de estudo, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 1</label>
+                    <caption>
+                        <title>Map with the location of the three study areas, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf01.tif"/>
+                </fig>
+            </fig-group>
+            <p>Composi&#x00E7;&#x00E3;o Flor&#x00ED;stica - No levantamento geral, foram amostrados 1020 indiv&#x00ED;duos, distribu&#x00ED;dos em 115 esp&#x00E9;cies, 80 g&#x00EA;neros e 45 fam&#x00ED;lias (<xref ref-type="table" rid="t2">tabela 2</xref>). A &#x00E1;rea B &#x00E9; mais rica, com 68 esp&#x00E9;cies, sendo 21% mais rica que C (56 spp.) e 26% mais rica que A (54 spp.).</p>
+            <p>As fam&#x00ED;lias mais ricas em esp&#x00E9;cies foram Myrtaceae (17 esp&#x00E9;cies), Lauraceae (12), Fabaceae (8), Rubiaceae e Meliaceae (5). As fam&#x00ED;lias mais abundantes em indiv&#x00ED;duos foram Euphorbiaceae (127 indiv&#x00ED;duos), Myrtaceae (115), Olacaceae (114), Rubiaceae (108) e Meliaceae (68).</p>
+            <table-wrap-group id="t2">
+                <table-wrap xml:lang="pt">
+                    <label>Tabela 2</label>
+                    <caption>
+                        <title>Composi&#x00E7;&#x00E3;o flor&#x00ED;stica nas tr&#x00EA;s &#x00E1;reas amostradas (A, B e C), Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil. Class. Sucess.: Classifica&#x00E7;&#x00E3;o Sucessional. PI: Pioneira, I: Secund&#x00E1;ria inicial, T: Secund&#x00E1;ria tardia, UM: Umbr&#x00F3;filas. Sindromes dispers&#x00E3;o. ZOO: Zooc&#x00F3;rica, ANE: Anemoc&#x00F3;rica, AUT: Autoc&#x00F3;rica.</title>
+                    </caption>
+                </table-wrap>
+                <table-wrap xml:lang="en">
+                    <label>Table 2</label>
+                    <caption>
+                        <title>Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.</title>
+                    </caption>
+                    <table>
+                        <thead>
+                            <tr>
+                                <th align="left">Fam&#x00ED;lia/Esp&#x00E9;cie</th>
+                                <th align="center">Nome Popular</th>
+                                <th align="center">&#x00C1;rea A</th>
+                                <th align="center">&#x00C1;rea B</th>
+                                <th align="center">&#x00C1;rea C</th>
+                                <th align="center">Class. Sucess.</th>
+                                <th align="center">Class. Sucess. (P-NP)</th>
+                                <th align="center">S&#x00ED;ndrome dispers&#x00E3;o</th>
+                                <th align="center">N&#x00BA; de coleta</th>
+                            </tr>
+                        </thead>
+                        <tbody>
+                            <tr>
+                                <td align="left">Anacardiaceae <italic>Schinus terebinthifolia</italic> Raddi</td>
+                                <td align="center">aroeira-pimenteira</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">103</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Annonaceae <italic>Annona dolabripetala</italic> Raddi</td>
+                                <td align="center">araticum</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">117</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Annona emarginata</italic> (Schltdl.) H.Rainer</td>
+                                <td align="center">araticum-mirim</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">55</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Annona sylvatica</italic> A.St.-Hil.</td>
+                                <td align="center">araticum-do-mato</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">59</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Apocynaceae <italic>Aspidosperma olivaceum</italic> M&#x00FC;ll.Arg.</td>
+                                <td align="center">guatambu</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">61</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Arecaceae <italic>Geonoma schottiana</italic> Mart.</td>
+                                <td align="center">guaricanga</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">74</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Syagrus romanzoffiana</italic> (Cham.) Glassman</td>
+                                <td align="center">jeriv&#x00E1;</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">88</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Asteraceae <italic>Piptocarpha macropoda</italic> (DC.) Baker</td>
+                                <td align="center">vassour&#x00E3;o</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ANE</td>
+                                <td align="center">97</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Bignoniaceae <italic>Jacaranda macrantha</italic> Cham.</td>
+                                <td align="center">carobinha</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">118</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Boraginaceae <italic>Cordia sellowiana</italic> Cham.</td>
+                                <td align="center">louro-mole</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">47</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Burseraceae <italic>Protium heptaphyllum</italic> (Aubl.) Marchand</td>
+                                <td align="center">almecegueira</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">130</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Cardiopteridaceae <italic>Citronella paniculata</italic> (Mart.) R.A.Howard</td>
+                                <td align="center">congonha</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">127</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Caricaceae <italic>Jacaratia heptaphylla&#x00A0;</italic>(Vell.) A.DC.</td>
+                                <td align="center">jaracati&#x00E1;</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">106</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Chrysobalanaceae <italic>Hirtella hebeclada</italic> Moric. ex DC.</td>
+                                <td align="center">vermelh&#x00E3;o</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">58</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Clusiaceae <italic>Tovomitopsis paniculata</italic> (Spreng.) Planch. &#x0026; Triana</td>
+                                <td align="center">azedinho</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">63</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Cyatheaceae <italic>Alsophila setosa</italic> Kaulf.</td>
+                                <td align="center">samambaia&#x00E7;u</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">57</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cyathea delgadii&#x00A0;</italic>Sternb.</td>
+                                <td align="center">samambaia&#x00E7;u</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">123</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Elaeocarpaceae <italic>Sloanea guianensis</italic> (Aubl.) Benth.</td>
+                                <td align="center">sapopemba</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">129</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Sloanea hirsuta</italic> (Schott) Planch. ex Benth.</td>
+                                <td align="center">ouri&#x00E7;o-do-mato</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">18</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Euphorbiaceae <italic>Alchornea triplinervia</italic> (Spreng.) M&#x00FC;ll.Arg.</td>
+                                <td align="center">tapi&#x00E1;-mirim</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">13</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Croton floribundus</italic> Spreng.</td>
+                                <td align="center">capixingui</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">93</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Croton macrobothrys</italic> Baill.</td>
+                                <td align="center">sangra d&#x00B4;&#x00E1;gua</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">60</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Sapium glandulosum</italic> (L.) Morong</td>
+                                <td align="center">leiteiro</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">124</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Fabaceae <italic>Senegalia polyphylla</italic> (DC.) Britton &#x0026; Rose</td>
+                                <td align="center">monjoleiro</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">108</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Bauhinia forficata</italic> Link</td>
+                                <td align="center">pata-de-vaca</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">95</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Copaifera trapezifolia</italic>&#x00A0;Hayne</td>
+                                <td align="center">copaiba-da-serra</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">121</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Dahlstedtia pinnata</italic> (Benth.) Malme</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">AUT</td>
+                                <td align="center">92</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Inga sessilis</italic> (Vell.) Mart.</td>
+                                <td align="center">ing&#x00E1;-ferradura</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">113</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Mimosa scabrella</italic> Benth.</td>
+                                <td align="center">bracatinga</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">05</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Piptadenia gonoacantha</italic> (Mart.) J.F.Macbr.</td>
+                                <td align="center">pau-jacar&#x00E9;</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">AUT</td>
+                                <td align="center">102</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Platymiscium floribundum</italic> Vogel</td>
+                                <td align="center">sacamb&#x00FA;</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">53</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Lauraceae <italic>Cinnamomum hirsutum</italic> (Lorea-Hern.) Van der Werff</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">125</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cinnamomum pseudoglaziovii</italic>&#x00A0;(Lorea-Hern.) Van der Werff</td>
+                                <td align="center">canela-garuva</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">23</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cryptocarya mandioccana</italic> Meisn.</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">56</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Endlicheria paniculata</italic> (Spreng.) J.F.Macbr.</td>
+                                <td align="center">canela-cheirosa</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">04</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Nectandra membranacea</italic> (Sw.) Griseb.</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">107</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Nectandra oppositifolia</italic> Nees</td>
+                                <td align="center">canela-ferrugem</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">33</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea glaziovii</italic> Mez</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">132</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea catharinensis</italic> Mez</td>
+                                <td align="center">canela-preta</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">52</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea koscinskii</italic> Baitello &#x0026; Brotto</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">70</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea</italic> aff. <italic>montana</italic> (Meisn.) Mez</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="left"/>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea puberula</italic> (Rich.) Nees</td>
+                                <td align="center">canela-mole</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">105</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ocotea silvestris</italic> V&#x00E1;ttimo-Gil</td>
+                                <td align="center">canela-branca</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">86</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Lecythidaceae <italic>Cariniana estrellensis</italic> (Raddi) Kuntze</td>
+                                <td align="center">jequitib&#x00E1;-branco</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">82</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Melastomataceae <italic>Miconia budlejoides</italic>Triana.</td>
+                                <td align="center">pixiririca</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">116</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Miconia cinnamomifolia</italic> (DC.) Naudin</td>
+                                <td align="center">jacatir&#x00E3;o</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">11</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Mouriri chamissoana</italic> Cogn.</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">31</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Pleroma granulosum</italic> (Desr.) D. Don</td>
+                                <td align="center">quaresmeira</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ANE</td>
+                                <td align="center">101</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Meliaceae <italic>Cabralea canjerana</italic> (Vell.) Mart.</td>
+                                <td align="center">canjerana</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">32</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cedrela fissilis</italic> Vell.</td>
+                                <td align="center">cedro rosa</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">89</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Guarea macrophylla</italic> Vahl ssp. <italic>tuberculata</italic> (Vell.) T.D.Penn.</td>
+                                <td align="center">marinheiro</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">24</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Trichilia pallens</italic> C.DC.</td>
+                                <td align="center">catigu&#x00E1;</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">79</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Trichilia silvatica</italic> C.DC.</td>
+                                <td align="center">catigu&#x00E1;</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">16</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Monimiaceae <italic>Mollinedia elegans</italic> Tul.</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">48</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Mollinedia schottiana</italic> (Spreng.) Perkins</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">01</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Mollinedia triflora</italic> (Spreng.) Tul.</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">131</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Mollinedia uleana</italic> Perkins</td>
+                                <td align="center">capixim</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">64</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Moraceae <italic>Ficus luschnathiana</italic> (Miq.) Miq.</td>
+                                <td align="center">figueira-branca</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">03</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Sorocea bonplandii</italic> (Baill.) W.C.Burger et al.</td>
+                                <td align="center">canxim</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">51</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Myristicaceae <italic>Virola bicuhyba</italic> (Schott ex Spreng.) Warb.</td>
+                                <td align="center">bicu&#x00ED;ba</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">12</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Myrtaceae <italic>Eugenia beaurepaireana</italic> (Kiaersk.) D.Legrand</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">90</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia cerasiflora</italic> Miq.</td>
+                                <td align="center">guamirim</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">38</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia cereja</italic> D.Legrand</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">62</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia involucrata</italic> DC.</td>
+                                <td align="center">cereja-do-rio-grande</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">68</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia prasina</italic> O.Berg</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">20</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia subterminalis</italic> DC.</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">19</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia supraaxillaris</italic> Spring</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">77</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Marlierea racemosa</italic> (Vell.) Kiaersk.</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">65</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia anacardiifolia</italic> Gardner</td>
+                                <td align="center">marmelinho</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">45</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia hebepetala</italic> DC.</td>
+                                <td align="center">guamirim</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">119</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia neobrasiliensis</italic> A.R.Louren&#x00E7;o &#x0026; E.Lucas</td>
+                                <td align="center">ara&#x00E7;arana</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">49</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia neolucida</italic> A.R.Louren&#x00E7;o &#x0026; E.Lucas</td>
+                                <td align="center">ara&#x00E7;arana</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">28</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia splendens</italic> (Sw.) DC.</td>
+                                <td align="center">guamirim</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">54</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia tenuivenosa</italic> Kiaersk.</td>
+                                <td align="center">cambu&#x00ED;</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">91</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia tijucensis</italic> Kiaersk.</td>
+                                <td align="center">guamirim-ferro</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">84</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia tomentosa</italic> (Aubl.) DC.</td>
+                                <td align="center">goiaba-brava</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">39</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrcia</italic> sp.</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">54</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Nyctaginaceae <italic>Guapira opposita</italic> (Vell.) Reitz</td>
+                                <td align="center">maria-mole</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">08</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Olacaceae <italic>Heisteria silvianii</italic> Schwacke</td>
+                                <td align="center">brinco-de-mulata</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">14</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Oleaceae <italic>Chionanthus filiformis</italic> (Vell.) P.S.Green</td>
+                                <td align="center">azeitona-do-mato</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">35</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Peraceae <italic>Pera glabrata</italic> (Schott) Baill.</td>
+                                <td align="center">cabeluda-do-mato</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">120</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Phyllantaceae <italic>Hyeronima alchorneoides</italic> Allem&#x00E3;o</td>
+                                <td align="center">urucuruna</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">100</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Phytolaccaceae <italic>Seguieria langsdorffii</italic> Moq.</td>
+                                <td align="center">limoeiro-do-mato</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">112</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Picramniaceae <italic>Picramnia glazioviana</italic> Engl.</td>
+                                <td align="center">cafezinho</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">30</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Polygonaceae <italic>Ruprechtia laxiflora</italic> Meisn.</td>
+                                <td align="center">marmeleiro-do-mato</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">115</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Primulaceae <italic>Myrsine gardneriana</italic> A.DC.</td>
+                                <td align="center">capororoca</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">109</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Myrsine umbellata</italic> Mart.</td>
+                                <td align="center">capororoca</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">110</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Proteaceae <italic>Euplassa cantareirae</italic> Sleumer</td>
+                                <td align="center">carvalho-da-cantareira</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">50</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Rosaceae <italic>Prunus myrtifolia</italic> (L.) Urb.</td>
+                                <td align="center">pessegueiro-bravo</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">17</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Rubiaceae <italic>Cordiera myrciifolia</italic> (K.Schum.) CHPerss &#x0026; Delprete</td>
+                                <td align="center">marmelinho</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">87</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Posoqueria latifolia</italic> (Rudge) Schult.</td>
+                                <td align="center">baga-de-macaco</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">66</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Psychotria suterella</italic> M&#x00FC;ll.Arg.</td>
+                                <td align="center">pasto-d&#x2019;anta</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">22</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Psychotria vellosiana</italic> Benth.</td>
+                                <td align="center">erva-de-rato</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">46</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Rudgea gardenioides</italic> (Cham.) M&#x00FC;ll.Arg.</td>
+                                <td align="center">jasmim-do-mato</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">122</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Rutaceae <italic>Esenbeckia grandiflora</italic> Mart.</td>
+                                <td align="center">pau-de-cutia</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">AUT</td>
+                                <td align="center">67</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Salicaceae <italic>Casearia decandra</italic> Jacq.</td>
+                                <td align="center">gua&#x00E7;atonga</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">83</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Casearia obliqua</italic> Spreng.</td>
+                                <td align="center">gua&#x00E7;atonga</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">69</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Casearia sylvestris</italic> Sw.</td>
+                                <td align="center">erva de lagarto</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">94</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Sapindaceae <italic>Allophylus petiolulatus</italic> Radlk.</td>
+                                <td align="center">fruta-de-pombo</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">73</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cupania oblongifolia</italic> Mart.</td>
+                                <td align="center">cuvant&#x00E3;</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">09</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Matayba elaeagnoides</italic> Radlk.</td>
+                                <td align="center">camboat&#x00E1;-branco</td>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">76</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Matayba guianensis</italic> Aubl.</td>
+                                <td align="center">camboat&#x00E1;-branco</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">85</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Sapotaceae <italic>Chrysophyllum inornatum</italic> Mart.</td>
+                                <td align="center">aleixo</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">75</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Ecclinusa ramiflora</italic> Mart.</td>
+                                <td align="center">guac&#x00E1;</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">111</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Pouteria bullata</italic> (S.Moore) Baehni</td>
+                                <td align="center">guapeva</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">114</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Solanaceae <italic>Cestrum schlechtendalii</italic>. G.Don.</td>
+                                <td align="center">coerana</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">126</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Sessea brasiliensis</italic> Toledo</td>
+                                <td align="center">peroba-d&#x2019;&#x00E1;gua</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ANE</td>
+                                <td align="center">98</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Solanum pseudoquina</italic> A.St.-Hil.</td>
+                                <td align="center">quina-falsa</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">128</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Symplocaceae <italic>Symplocos variabilis</italic> Mart. ex Miq.</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">UM</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">71</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Thymelaeaceae <italic>Daphnopsis fasciculata</italic> (Meisn.) Nevling</td>
+                                <td align="center">embira-branca</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">T</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">82</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Urticaceae <italic>Urera baccifera</italic> (L.) Gaudich. ex Wedd.</td>
+                                <td align="center">urtiga</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">96</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cecropia glaziovii</italic> Snethl.</td>
+                                <td align="center">emba&#x00FA;ba-vermelha</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">PI</td>
+                                <td align="center">P</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">104</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Coussapoa microcarpa</italic> (Schott) Rizzini</td>
+                                <td align="center">mata-pau</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="left"/>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ZOO</td>
+                                <td align="center">10</td>
+                            </tr>
+                            <tr>
+                                <td align="left">Vochysiaceae <italic>Vochysia magnifica</italic> Warm.</td>
+                                <td align="center">guaricica</td>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">07</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Vochysia selloi</italic> Warm.</td>
+                                <td align="left"/>
+                                <td align="left"/>
+                                <td align="center">X</td>
+                                <td align="center">X</td>
+                                <td align="center">I</td>
+                                <td align="center">NP</td>
+                                <td align="center">ANE</td>
+                                <td align="center">78</td>
+                            </tr>
+                        </tbody>
+                    </table>
+                </table-wrap>
+            </table-wrap-group>
+            <p>Os g&#x00EA;neros mais ricos foram <italic>Eugenia, Myrcia</italic> e <italic>Ocotea</italic> (sete esp&#x00E9;cies cada), <italic>Mollinedia</italic> (quatro) e <italic>Annona</italic> e <italic>Casearia</italic> (tr&#x00EA;s cada).</p>
+            <p>Riqueza e Abund&#x00E2;ncia nas &#x00C1;reas A, B e C - Na &#x00C1;rea A foram amostrados 321 indiv&#x00ED;duos, 54 esp&#x00E9;cies e 26 fam&#x00ED;lias. As fam&#x00ED;lias com maior riqueza foram Myrtaceae (10 esp&#x00E9;cies), Lauraceae (6 esp.), Euphorbiaceae e Rubiaceae (4 esp.) e Monimiaceae (3 esp.). As fam&#x00ED;lias mais abundantes foram Rubiaceae (70 indiv&#x00ED;duos), Olacaceae (42 ind.), Myrtaceae (32 ind.), Clusiaceae (23 ind.) e Monimiaceae (20 ind.). As fam&#x00ED;lias Rubiaceae e Olacaceae destacam-se nas primeiras posi&#x00E7;&#x00F5;es quanto &#x00E0; abund&#x00E2;ncia, n&#x00E3;o ocorrendo o mesmo em rela&#x00E7;&#x00E3;o a riqueza, mostrando que a alta abund&#x00E2;ncia dessas fam&#x00ED;lias &#x00E9; por causa de uma esp&#x00E9;cie, <italic>Psychotria suterella</italic> em Rubiaceae e <italic>Heisteria silvianii</italic> em Olacaceae. Os g&#x00EA;neros mais ricos foram <italic>Myrcia</italic> (quatro esp&#x00E9;cies), <italic>Eugenia, Ocotea</italic> e <italic>Mollinedia</italic> (tr&#x00EA;s cada), <italic>Annona</italic> e <italic>Cinnamomum</italic> (duas cada). Podemos observar que dentre estas, somente <italic>Cinnamomum</italic> n&#x00E3;o se destacou nos resultados gerais.</p>
+            <p>A &#x00C1;rea B apresentou 399 indiv&#x00ED;duos, 68 esp&#x00E9;cies e 32 fam&#x00ED;lias. As fam&#x00ED;lias com maior riqueza foram Myrtaceae (10 esp&#x00E9;cies), Lauraceae (7 esp.), Meliaceae (5 esp.), Sapindaceae e Monimiaceae (4 esp.).</p>
+            <p>As fam&#x00ED;lias mais abundantes em n&#x00FA;mero de indiv&#x00ED;duos foram Myrtaceae (72 indiv&#x00ED;duos), Sapindaceae (39 ind.), Meliaceae (38 ind.), Olacaceae (37 ind.) e Rubiaceae (31 ind.). Nesta &#x00E1;rea, Sapindaceae e Meliaceae, destacaram-se tanto no levantamento por esp&#x00E9;cies quanto de indiv&#x00ED;duos. Os g&#x00EA;neros que se destacaram nesta &#x00E1;rea foram <italic>Eugenia</italic> (cinco esp&#x00E9;cies), <italic>Mollinedia, Myrcia</italic> e <italic>Ocotea</italic> (quatro esp&#x00E9;cies cada), tamb&#x00E9;m amostradas na &#x00E1;rea A, seguidas de <italic>Casearia</italic> (tr&#x00EA;s) e <italic>Matayba</italic> (duas). &#x00C1;rea C apresentou 300 indiv&#x00ED;duos pertencentes a 56 esp&#x00E9;cies e 30 fam&#x00ED;lias. As fam&#x00ED;lias mais ricas foram Fabaceae (7 esp&#x00E9;cies), Lauraceae (6 esp.), Euphorbiaceae e Myrtaceae (4 esp.) e Meliaceae (2 esp.). As fam&#x00ED;lias Fabaceae e Euphorbiaceae tamb&#x00E9;m foram as mais ricas no levantamento realizado na Floresta Ombr&#x00F3;fila Densa situada no munic&#x00ED;pio de Cunha - SP por <xref ref-type="bibr" rid="B1">Aguiar <italic>et al</italic>. (2001)</xref>. As fam&#x00ED;lias mais abundantes foram Euphorbiaceae (94 ind.), Olacaceae (35 ind.), Fabaceae (32 ind.), Meliaceae (16 ind.) e Lauraceae (15 ind). Em rela&#x00E7;&#x00E3;o aos g&#x00EA;neros, aqueles que mais se destacaram nesta an&#x00E1;lise foram <italic>Annona, Croton, Mollinedia, Myrcia, Myrsine, Nectandra, Ocotea</italic> e <italic>Vochysia</italic> (duas esp&#x00E9;cies cada), sendo que as quatro primeiras destacadas acima, apresentaram-se somente nesta &#x00E1;rea.</p>
+            <p>Ao compararmos as tr&#x00EA;s &#x00E1;reas de estudo, Olacaceae destaca-se pela abund&#x00E2;ncia nas tr&#x00EA;s &#x00E1;reas, entretanto Myrtaceae e Rubiaceae em duas delas. A alta representatividade de Olacaceae &#x00E9; devida a uma &#x00FA;nica esp&#x00E9;cie, <italic>H. silvianii</italic>, e Rubiaceae por <italic>P. suterella</italic>, enquanto que Myrtaceae, pela riqueza de esp&#x00E9;cies. Em rela&#x00E7;&#x00E3;o aos g&#x00EA;neros que mais se destacaram nas &#x00E1;reas estudadas, podemos observar que a &#x00E1;rea C foi aquela mais distinta dentre elas, pois nesta &#x00E1;rea n&#x00E3;o h&#x00E1; uma predomin&#x00E2;ncia de um g&#x00EA;nero.</p>
+            <p>Par&#x00E2;metros fitossociol&#x00F3;gicos - A <xref ref-type="table" rid="t3">tabela 3</xref> mostra os par&#x00E2;metros totais e por &#x00E1;rea, a &#x00E1;rea B apresentou 39% do n&#x00FA;mero total de indiv&#x00ED;duos amostrados, enquanto as &#x00E1;reas A e C, 31% e 30% respectivamente.</p>
+            <p>Na &#x00E1;rea A, <italic>H. silvianii</italic> (22,7%), <italic>Aspidosperma olivaceum</italic> (18,1%) e <italic>Euplassa cantareirae</italic> (10,4%), esp&#x00E9;cies secund&#x00E1;rias tardias, apresentaram os maiores valores de domin&#x00E2;ncia relativa. As esp&#x00E9;cies que destacaram pelo valor de densidade foram <italic>P. suterella</italic> (19,6%), <italic>H. silvianii</italic> (13,1%) e <italic>Tovomitopsis paniculata</italic> (7,1%).</p>
+            <p>Na &#x00E1;rea B, as esp&#x00E9;cies <italic>Alchornea triplinervia</italic> (22,6%), <italic>H. silvianii</italic> (11,1%), <italic>Cabralea canjerana</italic> (6,8%), <italic>Casearia obliqua</italic> (6,5%) e <italic>Platymiscium floribundum</italic> (6,4%) destacaram-se por seus valores de domin&#x00E2;ncia relativa. Dentre elas, <italic>H. silvianii</italic> &#x00E9; a &#x00FA;nica secund&#x00E1;ria tardia e tamb&#x00E9;m apresentou alto valor de domin&#x00E2;ncia na &#x00E1;rea A. Destacaram-se pelo valor de densidade, <italic>H. silvianii</italic> (9,3%), <italic>Cupania oblongifolia</italic> (8,8%), <italic>Myrcia tijucensis</italic> (7,3%) e <italic>P. suterella</italic> (7,0%).</p>
+            <p>Na &#x00E1;rea C, destacaram-se pelo valor de domin&#x00E2;ncia <italic>Piptadenia gonoacantha</italic> (26,50%), <italic>Croton floribundus</italic> (24,8%), <italic>A. triplinervia</italic> (10,4%) e <italic>Bauhinia forficata</italic> (6,8%). Destacaram-se pelo valor de densidade, <italic>C. floribundus</italic> (18,0%), <italic>H. silvianii</italic> (11,67%), <italic>A. triplinervia</italic> (7,7%) e <italic>P. gonoacantha</italic> (6,7%).</p>
+            <p>Ao comparar as tr&#x00EA;s &#x00E1;reas de estudo pelas esp&#x00E9;cies presentes, podemos constatar que as tr&#x00EA;s &#x00E1;reas amostradas apresentam estrutura e composi&#x00E7;&#x00E3;o flor&#x00ED;stica distintas. Algumas esp&#x00E9;cies aparecem nas tr&#x00EA;s &#x00E1;reas, mas em situa&#x00E7;&#x00F5;es diferentes, por exemplo, <italic>H. silvianii,</italic> destacou-se tanto na &#x00E1;rea A e B, por seu valor de domin&#x00E2;ncia, enquanto na &#x00E1;rea C, pela frequ&#x00EA;ncia, mostrando que nas duas primeiras &#x00E1;reas encontra-se no dossel, enquanto em C, nos estratos inferiores da floresta.</p>
+            <p>Ao comparar a densidade das tr&#x00EA;s &#x00E1;reas, constatamos que B (1995 ind./ha) &#x00E9; a mais densa, sendo 33% maior que C (1500 ind./ha) e 24% maior que A (1605 ind./ha). A maior densidade da &#x00E1;rea B pode ser explicada pelo predom&#x00ED;nio de secund&#x00E1;rias iniciais no dossel e pela grande quantidade de secund&#x00E1;rias tardias no sub-bosque, estas &#x00FA;ltimas, em fase de crescimento, com um grande n&#x00FA;mero de indiv&#x00ED;duos jovens com pequenos di&#x00E2;metros. Ao tratar-se de domin&#x00E2;ncia, o cen&#x00E1;rio muda, pois, a &#x00E1;rea C apresenta a menor domin&#x00E2;ncia (30,6 m<sup>2</sup> /ha), em compara&#x00E7;&#x00E3;o com as &#x00E1;reas A e B (45,4 m<sup>2</sup>/ha e 43,4 m<sup>2</sup>/ha, respectivamente), sendo 32,5% e 29,4% menor, respectivamente, enquanto os valores da &#x00E1;rea A e B s&#x00E3;o pr&#x00F3;ximos.</p>
+            <p>Os valores de DeA e DoA mostram que na &#x00E1;rea A, h&#x00E1; v&#x00E1;rios indiv&#x00ED;duos com grandes di&#x00E2;metros, mas estes pertencem a um mesmo grupo ecol&#x00F3;gico (secund&#x00E1;rias tardias), indicando que a &#x00E1;rea est&#x00E1; mais avan&#x00E7;ada na sucess&#x00E3;o. Na &#x00E1;rea B, as esp&#x00E9;cies com os maiores di&#x00E2;metros pertencem a mais de um grupo ecol&#x00F3;gico, principalmente as secund&#x00E1;rias iniciais e algumas tardias, devido &#x00E0; maior riqueza e ao maior n&#x00FA;mero de indiv&#x00ED;duos. Na &#x00E1;rea C, a situa&#x00E7;&#x00E3;o &#x00E9; bem distinta, pois tanto a DeA quanto a DoA tem valores baixos, quando comparados com A e B, indicando um maior n&#x00FA;mero de indiv&#x00ED;duos com di&#x00E2;metros menores.</p>
+            <p>An&#x00E1;lises grupos ecol&#x00F3;gicos - Na an&#x00E1;lise total de esp&#x00E9;cies, quanto aos seus respectivos grupos ecol&#x00F3;gico, as secund&#x00E1;rias tardias e iniciais mantiveram-se em propor&#x00E7;&#x00F5;es pr&#x00F3;ximas (33,9% e 29,6%, respectivamente), as umbr&#x00F3;filas com 20% e, as pioneiras, de menor riqueza de esp&#x00E9;cies, com 16,5%. Ao realizarmos as mesmas an&#x00E1;lises, com o n&#x00FA;mero de indiv&#x00ED;duos, os resultados permaneceram similares. Na an&#x00E1;lise por esp&#x00E9;cies pioneiras ou n&#x00E3;o-pioneiras, 46,1% s&#x00E3;o esp&#x00E9;cies pioneiras e 53,9% n&#x00E3;o-pioneiras e, analisando pelo n&#x00FA;mero de indiv&#x00ED;duos, 39,5% e 60,5% respectivamente, observando resultados diferentes.</p>
+            <p>Na &#x00E1;rea A, as esp&#x00E9;cies secund&#x00E1;rias tardias destacaram-se com 48,1% do total de esp&#x00E9;cies, seguidas das iniciais com 25,9%, umbr&#x00F3;filas com 22,2% e, por fim, as pioneiras com 3,7% (<xref ref-type="fig" rid="f2">figuras 2 a, b</xref>). Nas mesmas an&#x00E1;lises com o n&#x00FA;mero de indiv&#x00ED;duos, o que se diferenciou foram as esp&#x00E9;cies umbr&#x00F3;filas, apresentando aumento de 13,7%, em fun&#x00E7;&#x00E3;o da riqueza da esp&#x00E9;cie <italic>P. suterella</italic>. E o oposto ocorreu com as iniciais, pois houve uma diminui&#x00E7;&#x00E3;o de 11,3%. Na an&#x00E1;lise de esp&#x00E9;cies classificadas como pioneiras ou n&#x00E3;o pioneiras, a porcentagem foi de 70,4% e 29,6%, respectivamente, enquanto abund&#x00E2;ncia das esp&#x00E9;cies n&#x00E3;o-pioneiras foi 84,4% e pioneiras, 15,6%, do total de indiv&#x00ED;duos amostrados. Esses resultados mostram que as esp&#x00E9;cies pertencentes ao grupo das pioneiras n&#x00E3;o s&#x00E3;o muito representadas pelo n&#x00FA;mero de indiv&#x00ED;duos.</p>
+            <table-wrap-group id="t3">
+                <table-wrap xml:lang="pt">
+                    <label>Tabela 3</label>
+                    <caption>
+                        <title>Par&#x00E2;metros com valores totais e por &#x00E1;rea, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </table-wrap>
+                <table-wrap xml:lang="en">
+                    <label>Table 3</label>
+                    <caption>
+                        <title>Parameters with total values and by area, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <table>
+                        <thead>
+                            <tr>
+                                <th valign="bottom" align="left">Par&#x00E2;metros</th>
+                                <th align="center">Valores Totais</th>
+                                <th align="center">&#x00C1;rea A</th>
+                                <th align="center">&#x00C1;rea B</th>
+                                <th align="center">&#x00C1;rea C</th>
+                            </tr>
+                        </thead>
+                        <tbody>
+                            <tr>
+                                <td valign="bottom" align="left">N&#x00BA; de indiv&#x00ED;duos</td>
+                                <td align="center">1020</td>
+                                <td align="center">321</td>
+                                <td align="center">399</td>
+                                <td align="center">300</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">N&#x00BA; de esp&#x00E9;cies</td>
+                                <td align="center">115</td>
+                                <td align="center">54</td>
+                                <td align="center">68</td>
+                                <td align="center">56</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">N&#x00BA; de fam&#x00ED;lias</td>
+                                <td align="center">45</td>
+                                <td align="center">26</td>
+                                <td align="center">32</td>
+                                <td align="center">30</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">Densidade (ind./ha)</td>
+                                <td align="center">1700</td>
+                                <td align="center">1605</td>
+                                <td align="center">1995</td>
+                                <td align="center">1500</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">&#x00C1;rea basal total (m<sup>2</sup>)</td>
+                                <td align="center">23,88</td>
+                                <td align="center">9,079</td>
+                                <td align="center">8,677</td>
+                                <td align="center">6,124</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">Domin&#x00E2;ncia (m<sup>2</sup>/ha)</td>
+                                <td align="center">39,801</td>
+                                <td align="center">45,396</td>
+                                <td align="center">43,385</td>
+                                <td align="center">30,622</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">Indice Shannon-Wiener</td>
+                                <td align="center">3,82</td>
+                                <td align="center">3,27</td>
+                                <td align="center">3,55</td>
+                                <td align="center">3,42</td>
+                            </tr>
+                            <tr>
+                                <td valign="bottom" align="left">Equabilidade</td>
+                                <td align="center">0,805</td>
+                                <td align="center">0,797</td>
+                                <td align="center">0,84</td>
+                                <td align="center">0,82</td>
+                            </tr>
+                        </tbody>
+                    </table>
+                </table-wrap>
+            </table-wrap-group>
+            <p>Na &#x00E1;rea B, tanto as secund&#x00E1;rias iniciais quanto as tardias apresentaram 35,3% do total de esp&#x00E9;cies, em seguida, as esp&#x00E9;cies umbr&#x00F3;filas com 22,1% e, as pioneiras, com 7,3%. Nas an&#x00E1;lises apresentadas pelo n&#x00FA;mero de indiv&#x00ED;duos n&#x00E3;o ocorreram grandes modifica&#x00E7;&#x00F5;es, secund&#x00E1;rias tardias com 37,1%, iniciais, 35,1%, umbr&#x00F3;filas, 26,6%, e as pioneiras, 1,2%. Na an&#x00E1;lise quanto a pioneiras e n&#x00E3;o pioneiras, a riqueza de esp&#x00E9;cies n&#x00E3;o-pioneiras foi 57,3%, e pioneiras, 42,6%. Quanto ao n&#x00FA;mero de indiv&#x00ED;duos, as n&#x00E3;o-pioneiras apresentaram 63,7% e as pioneiras 36,3% (<xref ref-type="fig" rid="f3">figuras 3 a, b</xref>). Esses resultados s&#x00E3;o semelhantes quando comparamos as duas classifica&#x00E7;&#x00F5;es sucessionais. Nesta &#x00E1;rea h&#x00E1; maior n&#x00FA;mero de pioneiras em rela&#x00E7;&#x00E3;o &#x00E0; &#x00E1;rea A.</p>
+            <p>Na &#x00E1;rea C, as esp&#x00E9;cies secund&#x00E1;rias iniciais ainda predominam, com 32,1%, em seguida est&#x00E3;o as esp&#x00E9;cies pioneiras, com 28,57%, as secund&#x00E1;rias tardias, com 21,4% e, as umbr&#x00F3;filas, com 17,9%. Nas an&#x00E1;lises de abund&#x00E2;ncia, as pioneiras predominam com 40%, secund&#x00E1;rias iniciais, 29,3%, tardias, 19,7%, e umbr&#x00F3;filas, 11%. Nesta &#x00E1;rea ocorre o oposto das outras duas &#x00E1;reas, pois as pioneiras se destacam, sendo essa diferen&#x00E7;a mais expressiva nas an&#x00E1;lises por abund&#x00E2;ncia. As esp&#x00E9;cies pioneiras apresentaram 60,7% do total de esp&#x00E9;cies e as n&#x00E3;o-pioneiras 39,3%. J&#x00E1; a abund&#x00E2;ncia de pioneiras e n&#x00E3;o pioneiras foi 69,3% e 30,7% respectivamente (<xref ref-type="fig" rid="f4">figuras 4 a, b</xref>). De modo geral, essa &#x00E1;rea se diferencia das outras n&#x00E3;o s&#x00F3; pelo aumento das esp&#x00E9;cies que sobrevivem em condi&#x00E7;&#x00F5;es de luz, mas tamb&#x00E9;m a diminui&#x00E7;&#x00E3;o das esp&#x00E9;cies que vivem sobre condi&#x00E7;&#x00F5;es de sombra, mostrando assim, que se trata de uma &#x00E1;rea mais aberta, com dossel mais falho, facilitando a presen&#x00E7;a de luz direta no solo.</p>
+            <p>Na &#x00E1;rea A as esp&#x00E9;cies secund&#x00E1;rias tardias destacam-se pela domin&#x00E2;ncia, densidade e riqueza, revelando que as esp&#x00E9;cies desse est&#x00E1;gio est&#x00E3;o fortemente presentes no dossel da floresta como tamb&#x00E9;m nos estratos inferiores.</p>
+            <p>Na &#x00E1;rea B as esp&#x00E9;cies secund&#x00E1;rias iniciais destacam-se pela domin&#x00E2;ncia, por&#x00E9;m, nos par&#x00E2;metros densidade e riqueza, as iniciais se igualam com as tardias. Esses resultados mostram que o dossel nessa &#x00E1;rea &#x00E9; composto, principalmente, pelas iniciais. Nos estratos inferiores os dois grupos est&#x00E3;o fortemente presentes.</p>
+            <fig-group id="f2">
+                <fig xml:lang="pt">
+                    <label>Figura 2</label>
+                    <caption>
+                        <title>a. Riqueza e abund&#x00E2;ncia das esp&#x00E9;cies pioneiras, secund&#x00E1;rias iniciais, secund&#x00E1;rias tardias e ombr&#x00F3;filas na &#x00E1;rea A. b. Riqueza e abund&#x00E2;ncia das esp&#x00E9;cies pioneiras ou n&#x00E3;o-pioneiras na &#x00E1;rea A. Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 2</label>
+                    <caption>
+                        <title>a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf02.tif"/>
+                </fig>
+            </fig-group>
+            <p>Na &#x00E1;rea C ocorre o oposto, pois, as esp&#x00E9;cies pioneiras destacam-se pela domin&#x00E2;ncia, mostrando que nesse trecho as pioneiras est&#x00E3;o presentes no dossel, por&#x00E9;m nos par&#x00E2;metros de densidade e riqueza, as pioneiras perdem o p&#x00F3;dio, dando lugar para as esp&#x00E9;cies secund&#x00E1;rias e umbr&#x00F3;filas.</p>
+            <p>As esp&#x00E9;cies umbr&#x00F3;filas aumentam da &#x00E1;rea C para A, indicando que a &#x00E1;rea A est&#x00E1; em fase mais avan&#x00E7;ada de sucess&#x00E3;o, aumentando a predomin&#x00E2;ncia das esp&#x00E9;cies t&#x00ED;picas de sub-bosque neste estrato (<xref ref-type="fig" rid="f5">figuras 5 a, b, c</xref>).</p>
+            <p>Em complemento &#x00E0; an&#x00E1;lise da classifica&#x00E7;&#x00E3;o sucessional, foram elaborados perfis diagramas totais de cada uma delas, com a representa&#x00E7;&#x00E3;o dos indiv&#x00ED;duos amostrados seguindo a sequ&#x00EA;ncia da planilha de campo. Os indiv&#x00ED;duos indicados na colora&#x00E7;&#x00E3;o amarela s&#x00E3;o representados pelas pioneiras; verdes claras, secund&#x00E1;rias iniciais; verdes escuras, tardias; e as vermelhas, esp&#x00E9;cies umbr&#x00F3;filas.</p>
+            <p>Na &#x00E1;rea A, o dossel &#x00E9; predominantemente composto pelas tardias, no estrato intermedi&#x00E1;rio predominam as iniciais, enquanto no sub-bosque predominam esp&#x00E9;cies umbr&#x00F3;filas. Ocorreram tr&#x00EA;s indiv&#x00ED;duos de esp&#x00E9;cies pioneiras, desses, dois no estrato intermedi&#x00E1;rio em dire&#x00E7;&#x00E3;o ao dossel e um no sub-bosque (<xref ref-type="fig" rid="f6">figura 6</xref>).</p>
+            <p>Na &#x00E1;rea B, predominam secund&#x00E1;rias iniciais no dossel; no estrato intermedi&#x00E1;rio, al&#x00E9;m das iniciais, tamb&#x00E9;m ocorrem as tardias; o sub-bosque t&#x00EA;m representantes de todos os grupos sucessionais, mas com baixa representatividade das pioneiras, com apenas cinco indiv&#x00ED;duos (<xref ref-type="fig" rid="f7">figura 7</xref>).</p>
+            <p>Na &#x00E1;rea C, h&#x00E1; predom&#x00ED;nio das pioneiras no dossel, cuja altura &#x00E9; mais baixa que A e B. J&#x00E1; no estrato intermedi&#x00E1;rio predominam pioneiras e secund&#x00E1;rias iniciais e, no sub-bosque, est&#x00E3;o presentes esp&#x00E9;cies pioneiras, secund&#x00E1;rias iniciais e tardias, havendo poucas esp&#x00E9;cies umbr&#x00F3;filas (<xref ref-type="fig" rid="f8">figura 8</xref>).</p>
+            <p>De modo geral, observa-se que as tr&#x00EA;s &#x00E1;reas s&#x00E3;o distintas, pois, na &#x00E1;rea A, as esp&#x00E9;cies est&#x00E3;o distribu&#x00ED;das conforme o esperado para um final de sucess&#x00E3;o, com o predom&#x00ED;nio das secund&#x00E1;rias tardias no dossel; j&#x00E1; na &#x00E1;rea B, ocorre o predom&#x00ED;nio das secund&#x00E1;rias iniciais no dossel e, nos outros estratos, h&#x00E1; todos os grupos sucessionais presentes, resultando em um grande n&#x00FA;mero de indiv&#x00ED;duos e, na &#x00E1;rea C, as pioneiras est&#x00E3;o bem representadas em todos os estratos.</p>
+            <fig-group id="f3">
+                <fig xml:lang="pt">
+                    <label>Figura 3</label>
+                    <caption>
+                        <title>a. Riqueza e abund&#x00E2;ncia das esp&#x00E9;cies pioneiras, secund&#x00E1;rias iniciais e tardias e ombr&#x00F3;filas na &#x00E1;rea B. b. Riqueza e abund&#x00E2;ncia das esp&#x00E9;cies pioneiras ou n&#x00E3;o-pioneiras na &#x00E1;rea B. Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 3</label>
+                    <caption>
+                        <title>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf03.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f4">
+                <fig xml:lang="pt">
+                    <label>Figura 4</label>
+                    <caption>
+                        <title>a. Riqueza e abund&#x00E2;ncia sucessional das esp&#x00E9;cies pioneiras, secund&#x00E1;rias iniciais e tardias e ombr&#x00F3;filas na &#x00E1;rea C. b. Riqueza e abund&#x00E2;ncia das esp&#x00E9;cies - pioneiras ou n&#x00E3;o-pioneiras na &#x00E1;rea C. Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 4</label>
+                    <caption>
+                        <title>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf04.tif"/>
+                </fig>
+            </fig-group>
+            <p>Com base na distribui&#x00E7;&#x00E3;o dos grupos sucessionais, a &#x00E1;rea A est&#x00E1; em est&#x00E1;gio mais avan&#x00E7;ado ou final na sucess&#x00E3;o, a &#x00E1;rea B em um est&#x00E1;gio intermedi&#x00E1;rio e, &#x00E1;rea C, em est&#x00E1;gio mais inicial.</p>
+            <p>Estratifica&#x00E7;&#x00E3;o florestal e distribui&#x00E7;&#x00E3;o diam&#x00E9;trica - Na &#x00E1;rea A, aproximadamente 64% (204) dos indiv&#x00ED;duos amostrados apresentam at&#x00E9; 12 m de altura, 17% (59 ind.) entre 12,1 e 20 m, 15% entre 20,1 e 28 m e 4% entre 28,1 e 36 m (21 ind.). Essa distribui&#x00E7;&#x00E3;o de indiv&#x00ED;duos apresenta formato de &#x201C;J invertido&#x201D; (maior n&#x00FA;mero de indiv&#x00ED;duos nas menores classes de altura, diminuindo nas maiores classes). A grande concentra&#x00E7;&#x00E3;o de indiv&#x00ED;duos na primeira classe de altura deve-se pela abund&#x00E2;ncia das esp&#x00E9;cies umbr&#x00F3;filas, principalmente <italic>P. suterella</italic> (<xref ref-type="fig" rid="f9">figura 9</xref>).</p>
+            <p>Na &#x00E1;rea B, aproximadamente 59% (238) dos indiv&#x00ED;duos amostrados apresentam at&#x00E9; 12 m de altura, 25% (102 ind.) entre 12,1 e 20 m, 12% entre 20,1 e 28 m. e 4% entre 28,1 e 36 m (59 ind.). Poucos indiv&#x00ED;duos passam dos 30 metros de altura (<xref ref-type="fig" rid="f10">figura 10</xref>).</p>
+            <p>J&#x00E1; na &#x00E1;rea C, aproximadamente 65% (196) dos indiv&#x00ED;duos amostrados apresentam at&#x00E9; 12 m de altura, 28% (83 ind.) entre 12,1 e 20 m. e 7% (21 ind.) acima dos 20 m. (<xref ref-type="fig" rid="f11">figura 11</xref>).</p>
+            <p>Ao compararmos as tr&#x00EA;s &#x00E1;reas de estudo, quanto &#x00E0; distribui&#x00E7;&#x00E3;o das classes de altura, podemos constatar que as &#x00E1;reas A e B s&#x00E3;o similares quanto &#x00E0; porcentagem dos indiv&#x00ED;duos em diferentes estratos. Em ambas as &#x00E1;reas h&#x00E1; a predomin&#x00E2;ncia das secund&#x00E1;rias tardias e iniciais nos diferentes estratos, com exce&#x00E7;&#x00E3;o do sub-bosque que em A possui exclusivamente esp&#x00E9;cies deste estrato (umbr&#x00F3;filas), enquanto em B ocorrem tamb&#x00E9;m indiv&#x00ED;duos jovens de esp&#x00E9;cies secund&#x00E1;rias. Por outro lado, na &#x00E1;rea C, a porcentagem dos indiv&#x00ED;duos na classe at&#x00E9; 12 m de altura &#x00E9; bem menor em rela&#x00E7;&#x00E3;o &#x00E0;s &#x00E1;reas A e B; as esp&#x00E9;cies pioneiras est&#x00E3;o representadas em todos os estratos dessa floresta e, no sub-bosque h&#x00E1; representantes de todas as categorias sucessionais.</p>
+            <p>Similaridade, agrupamento e ordena&#x00E7;&#x00E3;o entre as &#x00E1;reas de estudo - Na an&#x00E1;lise utilizando o coeficiente Canberra (UPGMA), as parcelas de um mesmo bloco mant&#x00EA;m-se de uma forma geral em um mesmo grupo, confirmando que as &#x00E1;reas de estudo (A, B e C) diferem entre si. No primeiro grupo, onde se encontram as parcelas da &#x00E1;rea A, h&#x00E1; somente uma &#x00FA;nica parcela (12) que pertence a B; por&#x00E9;m o segundo e o terceiro grupos reconhecidos nesta an&#x00E1;lise re&#x00FA;nem exclusivamente parcelas das &#x00E1;reas B e C respectivamente (<xref ref-type="fig" rid="f12">figura 12</xref>). O agrupamento da parcela 12 (&#x00E1;rea B) com as parcelas 1 a 10 (&#x00E1;rea A), pode ser explicada como uma parcela cuja floresta est&#x00E1; em fase mais final de sucess&#x00E3;o. &#x00C9; comum nas florestas ter parcelas em fases distintas, podendo ser causadas pela presen&#x00E7;a de uma mancha mais antiga, clareiras ou efeitos de borda. As an&#x00E1;lises de ordena&#x00E7;&#x00E3;o e classifica&#x00E7;&#x00E3;o mostram esses efeitos.</p>
+            <fig-group id="f5">
+                <fig xml:lang="pt">
+                    <label>Figura 5</label>
+                    <caption>
+                        <title>a. Domin&#x00E2;ncia relativa (DoR) das esp&#x00E9;cies. Colora&#x00E7;&#x00E3;o amarela: pioneira, verde clara: secund&#x00E1;ria inicial, verde escura: secund&#x00E1;ria tardia, vermelha: umbr&#x00F3;fila. b. Densidade relativa (DeR) das esp&#x00E9;cies amostradas. Colora&#x00E7;&#x00E3;o amarela: pioneira, verde clara: secund&#x00E1;ria inicial, verde escura: secund&#x00E1;ria tardia, vermelha: umbr&#x00F3;fila. c. Riqueza das esp&#x00E9;cies amostradas. Colora&#x00E7;&#x00E3;o amarela: pioneira, verde clara: secund&#x00E1;ria inicial, verde escura: secund&#x00E1;ria tardia, vermelha: umbr&#x00F3;fila. Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 5</label>
+                    <caption>
+                        <title>a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf05.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f6">
+                <fig xml:lang="pt">
+                    <label>Figura 6</label>
+                    <caption>
+                        <title>Diagrama de perfil da &#x00C1;rea A, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 6</label>
+                    <caption>
+                        <title>Profile diagram of Area A, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf06.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f7">
+                <fig xml:lang="pt">
+                    <label>Figura 7</label>
+                    <caption>
+                        <title>Diagrama de perfil da &#x00C1;rea B, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 7</label>
+                    <caption>
+                        <title>Profile diagram of Area B, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf07.tif"/>
+                </fig>
+            </fig-group>
+            <p>Na an&#x00E1;lise de ordena&#x00E7;&#x00E3;o, utilizou-se a An&#x00E1;lise de Correspond&#x00EA;ncia (CA) e a matriz de n&#x00FA;mero de indiv&#x00ED;duos por esp&#x00E9;cie. Os eixos 1, 2 e 3 correspondem a 11,8, 8,5 e 6,1 por cento da in&#x00E9;rcia total encontrada, totalizando-se 26,4%. Podemos observar que as parcelas da &#x00E1;rea C est&#x00E3;o separadas em todos os eixos (plano horizontal e vertical), sendo esta a mais diferente em rela&#x00E7;&#x00E3;o &#x00E0;s demais. As &#x00E1;reas A e B est&#x00E3;o separadas mais no eixo 2 (plano horizontal), ou seja, em rela&#x00E7;&#x00E3;o ao n&#x00FA;mero de indiv&#x00ED;duos, est&#x00E3;o mais pr&#x00F3;ximas, possivelmente devido &#x00E0;s esp&#x00E9;cies tardias j&#x00E1; estarem presentes nos estratos inferiores da &#x00E1;rea B (<xref ref-type="fig" rid="f13">figuras 13</xref> to <xref ref-type="fig" rid="f14">14</xref>).</p>
+            <p>Tanto as an&#x00E1;lises de classifica&#x00E7;&#x00E3;o quanto as de ordena&#x00E7;&#x00E3;o mostram, de uma forma geral, a forma&#x00E7;&#x00E3;o de tr&#x00EA;s grupos que correspondem &#x00E0;s tr&#x00EA;s &#x00E1;reas de estudo, havendo maior proximidade entre as &#x00E1;reas A e B devido a uma maior presen&#x00E7;a das esp&#x00E9;cies tardias em ambas as &#x00E1;reas.</p>
+            <p>S&#x00ED;ndrome de dispers&#x00E3;o - As esp&#x00E9;cies zooc&#x00F3;ricas destacaram-se em todas as &#x00E1;reas estudadas, A, B e C (85%, 88% e 70%, respectivamente). As anemoc&#x00F3;ricas apresentaram valores mais altos na &#x00E1;rea C, em virtude do maior n&#x00FA;mero de pioneiras encontradas nesta &#x00FA;ltima. J&#x00E1; as autoc&#x00F3;ricas est&#x00E3;o em menor n&#x00FA;mero na &#x00E1;rea B.</p>
+            <p>Esp&#x00E9;cies amea&#x00E7;adas de extin&#x00E7;&#x00E3;o - Do total de 115 esp&#x00E9;cies apuradas neste estudo, conforme consta na <xref ref-type="table" rid="t4">tabela 4</xref>, sete esp&#x00E9;cies (6,1%) enquadram-se em uma das categorias de grau de amea&#x00E7;a nas tr&#x00EA;s listas existentes. <italic>Ocotea catharinensis,</italic> presente nas tr&#x00EA;s &#x00E1;reas de estudo, est&#x00E1; como vulner&#x00E1;vel (VU) nas listas de S&#x00E3;o Paulo, do Brasil e IUCN; <italic>Cedrela fissilis</italic>, presente somente na &#x00E1;rea B, apresentou-se como VU nas listas de S&#x00E3;o Paulo e do Brasil, e em perigo (EN) na lista da IUCN; <italic>Trichilia silvatica</italic>, presente nas &#x00E1;reas A e B, e <italic>Eugenia prasina</italic>, na &#x00E1;rea B, est&#x00E3;o representadas como VU somente na lista da IUCN; <italic>Virola bicuhyba</italic> presente somente na &#x00E1;rea B, encontra-se EN nas listas de S&#x00E3;o Paulo e do Brasil; <italic>Pouteria bullata</italic>, presente somente na &#x00E1;rea B, &#x00E9; considerada EN na lista de S&#x00E3;o Paulo e Brasil e VU na lista da IUCN; <italic>E. cantareirae</italic> presente somente na &#x00E1;rea A, na lista do Brasil est&#x00E1; como EN e na lista de S&#x00E3;o Paulo est&#x00E1; como extinta (EX).</p>
+            <fig-group id="f8">
+                <fig xml:lang="pt">
+                    <label>Figura 8</label>
+                    <caption>
+                        <title>Diagrama de perfil da &#x00C1;rea C, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 8</label>
+                    <caption>
+                        <title>Profile diagram of Area C, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf08.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f9">
+                <fig xml:lang="pt">
+                    <label>Figura 9</label>
+                    <caption>
+                        <title>Distribui&#x00E7;&#x00E3;o dos indiv&#x00ED;duos em classes de altura na &#x00E1;rea A, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 9</label>
+                    <caption>
+                        <title>Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf09.tif"/>
+                </fig>
+            </fig-group>
+        </sec>
+        <sec sec-type="discussion">
+            <title>Discuss&#x00E3;o</title>
+            <p>Composi&#x00E7;&#x00E3;o Flor&#x00ED;stica - As fam&#x00ED;lias Myrtaceae e Lauraceae tamb&#x00E9;m foram as mais ricas em outros estudos realizados na Floresta Ombr&#x00F3;fila Densa Montana no Estado de S&#x00E3;o Paulo por <xref ref-type="bibr" rid="B8">Baitello <italic>et al</italic>. (1993)</xref>, <xref ref-type="bibr" rid="B26">Garcia &#x0026; Pirani (2001)</xref>, <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref>, <xref ref-type="bibr" rid="B2">Alves &#x0026; Metzger (2006)</xref>, <xref ref-type="bibr" rid="B43">Ogata &#x0026; Gomes (2006)</xref>, <xref ref-type="bibr" rid="B37">Lima <italic>et al</italic>. (2011)</xref>, <xref ref-type="bibr" rid="B5">Arzolla (2002</xref>, <xref ref-type="bibr" rid="B6">2011</xref>) e <xref ref-type="bibr" rid="B10">Barretto (2013)</xref>, trabalhos realizados no munic&#x00ED;pio de S&#x00E3;o Paulo e arredores, e no interior do Estado, por <xref ref-type="bibr" rid="B30">Ivanauskas (1997)</xref>, <xref ref-type="bibr" rid="B1">Aguiar <italic>et al</italic>. (2001)</xref>, <xref ref-type="bibr" rid="B52">Sztutman &#x0026; Rodrigues (2002)</xref> e <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref>, sendo que neste &#x00FA;ltimo estudo somente Myrtaceae destacou-se pela sua riqueza.</p>
+            <p>Os g&#x00EA;neros <italic>Cinnamomum, Eugenia, Mollinedia, Myrcia</italic> e <italic>Ocotea</italic> tamb&#x00E9;m se destacaram em outros levantamentos realizados no PEC por <xref ref-type="bibr" rid="B5">Arzolla (2002</xref>, <xref ref-type="bibr" rid="B6">2011</xref>), <italic>Nectandra</italic> tamb&#x00E9;m se destacou no levantamento realizado no PEC por <xref ref-type="bibr" rid="B5">Arzolla (2002)</xref>, <italic>Eugenia, Myrcia</italic> e <italic>Ocotea</italic>, por <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref>, <xref ref-type="bibr" rid="B37">Lima <italic>et al</italic>. (2011)</xref> e <xref ref-type="bibr" rid="B10">Barretto (2013)</xref> em remanescentes de Floresta Ombr&#x00F3;fila Densa Montana situados na regi&#x00E3;o metropolitana de S&#x00E3;o Paulo, <italic>Eugenia</italic> e <italic>Ocotea,</italic> por <xref ref-type="bibr" rid="B1">Aguiar <italic>et al</italic>. (2001)</xref> na regi&#x00E3;o de Cunha e somente <italic>Eugenia</italic> por <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref> no munic&#x00ED;pio de Miracatu.</p>
+            <fig-group id="f10">
+                <fig xml:lang="pt">
+                    <label>Figura 10</label>
+                    <caption>
+                        <title>Distribui&#x00E7;&#x00E3;o dos indiv&#x00ED;duos em classes de altura na &#x00E1;rea B, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 10</label>
+                    <caption>
+                        <title>Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf10.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f11">
+                <fig xml:lang="pt">
+                    <label>Figura 11</label>
+                    <caption>
+                        <title>Distribui&#x00E7;&#x00E3;o dos indiv&#x00ED;duos em classes de altura na &#x00E1;rea C, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 11</label>
+                    <caption>
+                        <title>Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf11.tif"/>
+                </fig>
+            </fig-group>
+            <p>Par&#x00E2;metros fitossociol&#x00F3;gicos - Os valores totais, desde estudo, de densidade absoluta de 1700 ind. ha<sup>-1</sup> e domin&#x00E2;ncia absoluta de 39,8 m<sup>2</sup> ha<sup>-1</sup> s&#x00E3;o compat&#x00ED;veis com os encontrados em outros trechos do PEC (<xref ref-type="bibr" rid="B8">Baitello <italic>et al</italic>. 1993</xref>, <xref ref-type="bibr" rid="B5">Arzolla 2002</xref>), onde a densidade absoluta variou entre 1248 a 2295 ind./ha e a domin&#x00E2;ncia entre 35,7 a 48,4 m<sup>2</sup> ha<sup>-1</sup>. Em estudo realizado em S&#x00E3;o Paulo e nos munic&#x00ED;pios vizinhos de Cotia e Itapevi (<xref ref-type="bibr" rid="B10">Barretto 2013</xref>) os valores de densidade variaram entre 1425 a 1760 ind. ha<sup>-1</sup> e de domin&#x00E2;ncia entre 44,5 a 49,3 m<sup>2</sup> ha<sup>-1</sup>, tamb&#x00E9;m compat&#x00ED;veis com os do presente estudo.</p>
+            <p>Em outros trechos da floresta do PEC estudados por <xref ref-type="bibr" rid="B5">Arzolla (2002)</xref>, tamb&#x00E9;m foram encontradas <italic>H. silvianii</italic> e <italic>A. olivaceum</italic> entre as esp&#x00E9;cies mais dominantes, e em Itapevi, somente <italic>H. silvianii</italic> (<xref ref-type="bibr" rid="B10">Barretto 2013</xref>). <xref ref-type="bibr" rid="B33">Klein (1990)</xref> destaca <italic>A. olivaceum</italic> como uma das esp&#x00E9;cies mais importantes nas encostas das Serras do Sul do pa&#x00ED;s e cita que <italic>E. cantareirae</italic> est&#x00E1; associada a florestas em sucess&#x00E3;o avan&#x00E7;ada. Sendo que esta tamb&#x00E9;m se destacou no estudo realizado no PEC por <xref ref-type="bibr" rid="B8">Baitello <italic>et al</italic>. (1993)</xref>. Ainda, <xref ref-type="bibr" rid="B13">Blum &#x0026; Roderjan (2007)</xref> citam a <italic>E. cantareirae</italic> como esp&#x00E9;cie indicadora de forma&#x00E7;&#x00E3;o de Floresta Ombr&#x00F3;fila Densa Montana.</p>
+            <p>A esp&#x00E9;cie <italic>P. suterella</italic> tamb&#x00E9;m se destacou em outros fragmentos do PEC (<xref ref-type="bibr" rid="B5">Arzolla 2002</xref>) e na Floresta Ombr&#x00F3;fila Densa Montana das encostas de Paranapiacaba (<xref ref-type="bibr" rid="B37">Lima <italic>et al</italic>. 2011</xref>), sendo que <xref ref-type="bibr" rid="B12">Bertani (2006)</xref> relata que essa esp&#x00E9;cie frequentemente se destaca pelo seu valor de densidade nos fragmentos florestais do Estado de S&#x00E3;o Paulo.</p>
+            <p><italic>A. triplinervia, H. silvianii, C. canjerana, C. obliqua</italic> e <italic>P. floribundum</italic> destacaram-se por seus valores de domin&#x00E2;ncia em outros trechos do PEC (<xref ref-type="bibr" rid="B5">Arzolla 2002</xref>). Em alguns levantamentos realizados no Estado de S&#x00E3;o Paulo, <italic>A. triplinervia</italic> destacou-se pelo seu valor de import&#x00E2;ncia (<xref ref-type="bibr" rid="B30">Ivanauskas 1997</xref>, <xref ref-type="bibr" rid="B5">Arzolla 2002</xref>, <xref ref-type="bibr" rid="B10">Barretto 2013</xref>). Esta esp&#x00E9;cie ocorre somente na forma de indiv&#x00ED;duos mais velhos nas florestas mais maduras, geralmente esparsos, sendo, por isso, rara, pois n&#x00E3;o se v&#x00EA; na regenera&#x00E7;&#x00E3;o (<xref ref-type="bibr" rid="B32">Klein 1984</xref>, <xref ref-type="bibr" rid="B33">1990</xref>). Na &#x00E1;rea de estudo, n&#x00E3;o foram observados indiv&#x00ED;duos jovens desta esp&#x00E9;cie. No levantamento realizado por <xref ref-type="bibr" rid="B17">Catharino <italic>et al</italic>. (2006)</xref>, dentre essas esp&#x00E9;cies, somente <italic>C. obliqua</italic> se assemelha com este estudo.</p>
+            <fig-group id="f12">
+                <fig xml:lang="pt">
+                    <label>Figura 12</label>
+                    <caption>
+                        <title>An&#x00E1;lise de classifica&#x00E7;&#x00E3;o das parcelas das tr&#x00EA;s &#x00E1;reas de estudo, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil., pelo m&#x00E9;todo UPGMA e coeficiente Canberra. Coeficiente de correla&#x00E7;&#x00E3;o igual a 0,7821.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 12</label>
+                    <caption>
+                        <title>Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf12.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f13">
+                <fig xml:lang="pt">
+                    <label>Figura 13</label>
+                    <caption>
+                        <title>Eixos 1 e 2 da an&#x00E1;lise de ordena&#x00E7;&#x00E3;o pelo m&#x00E9;todo CA das tr&#x00EA;s &#x00E1;reas de estudo, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 13</label>
+                    <caption>
+                        <title>Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf13.tif"/>
+                </fig>
+            </fig-group>
+            <fig-group id="f14">
+                <fig xml:lang="pt">
+                    <label>Figura 14</label>
+                    <caption>
+                        <title>Eixos 1 e 3 da an&#x00E1;lise de ordena&#x00E7;&#x00E3;o pelo m&#x00E9;todo CA das tr&#x00EA;s &#x00E1;reas de estudo, Parque Estadual da Cantareira, S&#x00E3;o Paulo, SP, Brasil.</title>
+                    </caption>
+                </fig>
+                <fig xml:lang="en">
+                    <label>Figure 14</label>
+                    <caption>
+                        <title>Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, S&#x00E3;o Paulo, S&#x00E3;o Paulo State, Brasil.</title>
+                    </caption>
+                    <graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="2236-8906-hoehnea-49-e1082020-gf14.tif"/>
+                </fig>
+            </fig-group>
+            <p><italic>C. oblongifolia</italic> destacou-se nos levantamentos de <xref ref-type="bibr" rid="B5">Arzolla (2002</xref>, <xref ref-type="bibr" rid="B6">2011</xref>) e <xref ref-type="bibr" rid="B10">Barretto (2013)</xref>. Em outro trecho estudado por <xref ref-type="bibr" rid="B6">Arzolla (2011)</xref>, <italic>C. floribundus</italic> e <italic>A. triplinervia</italic> tamb&#x00E9;m se destacaram. <italic>Piptocarpha macropoda</italic> tamb&#x00E9;m foi encontrada em alta frequ&#x00EA;ncia em trecho do PEC (<xref ref-type="bibr" rid="B6">Arzolla 2011</xref>) e no levantamento feito por <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref> na Floresta Ombr&#x00F3;fila Densa do Vale do Ribeira</p>
+            <p>An&#x00E1;lises grupos ecol&#x00F3;gicos - No estudo realizado por <xref ref-type="bibr" rid="B10">Barretto (2013)</xref>, em seu levantamento geral de esp&#x00E9;cies tardias, a percentagem apresentou o dobro do que encontrado neste estudo. Mas essa diferen&#x00E7;a pode ser pelo fato de que o autor considerou as esp&#x00E9;cies umbr&#x00F3;filas como parte das secund&#x00E1;rias tardias.</p>
+            <p>Em outro estudo realizado no PEC por <xref ref-type="bibr" rid="B5">Arzolla (2002)</xref>, as tardias destacaram-se tr&#x00EA;s vezes a mais que as iniciais, mas lembrando que o autor considerou tamb&#x00E9;m naquele trabalho, assim como Barretto, as umbr&#x00F3;filas como parte das esp&#x00E9;cies tardias.</p>
+            <p>O trabalho realizado por <xref ref-type="bibr" rid="B25">Gandolfi <italic>et al</italic>. (1995)</xref>, apresentou 30% de esp&#x00E9;cies pioneiras, sugerindo que o trecho estudado pelo autor se encontrava numa condi&#x00E7;&#x00E3;o inicial em termos sucessionais. Nos estudos de <xref ref-type="bibr" rid="B6">Arzolla (2011)</xref> e <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref>, as pioneiras tamb&#x00E9;m obtiveram percentagem expressivas (61% e 26%, respectivamente), mas os trechos referem-se a &#x00E1;reas de regenera&#x00E7;&#x00E3;o.</p>
+            <p><xref ref-type="bibr" rid="B10">Barretto (2013)</xref>, em suas an&#x00E1;lises, constatou nas tr&#x00EA;s &#x00E1;reas estudadas por ele, em fase avan&#x00E7;ada de sucess&#x00E3;o, alta domin&#x00E2;ncia e riqueza das esp&#x00E9;cies secund&#x00E1;rias tardias, assim como observado na &#x00E1;rea A deste estudo.</p>
+            <p>S&#x00ED;ndrome de dispers&#x00E3;o - Em outros levantamentos realizados na Floresta Ombr&#x00F3;fila Densa por <xref ref-type="bibr" rid="B17">Catharino <italic>et al.</italic> (2006)</xref>, <xref ref-type="bibr" rid="B37">Lima <italic>et al.</italic> (2011)</xref>, <xref ref-type="bibr" rid="B10">Barretto (2013)</xref>, <xref ref-type="bibr" rid="B40">Moura &#x0026; Mantovani (2017)</xref> foram encontrados resultados semelhantes quanto &#x00E0; porcentagem de esp&#x00E9;cies zooc&#x00F3;ricas. <xref ref-type="bibr" rid="B37">Lima <italic>et al.</italic> (2011)</xref> relata que nas &#x00E1;reas que desenvolveu seu estudo predominam esp&#x00E9;cies zooc&#x00F3;ricas, sendo &#x00E1;reas maduras da Floresta Ombr&#x00F3;fila Densa Montana das encostas da Serra do Mar em Santo Andr&#x00E9;, e <xref ref-type="bibr" rid="B39">Mantovani (1998)</xref> relata que &#x00E9; comum a predomin&#x00E2;ncia de esp&#x00E9;cies zooc&#x00F3;ricas nessas florestas.</p>
+            <p>Esp&#x00E9;cies amea&#x00E7;adas de extin&#x00E7;&#x00E3;o - A esp&#x00E9;cie <italic>E. cantareirae</italic> foi classificada como vulner&#x00E1;vel (VU) no estudo realizado por <xref ref-type="bibr" rid="B50">Souza <italic>et al</italic>. (2016)</xref>, o que diverge com a lista atualizada de flora amea&#x00E7;ada do Estado de S&#x00E3;o Paulo, publicada no Di&#x00E1;rio Oficial de S&#x00E3;o Paulo - Poder Executivo - Se&#x00E7;&#x00E3;o I - de 07 de junho de 2016, na qual consta como extinta (EX). Essa esp&#x00E9;cie &#x00E9; considerada rara, no entanto tal classifica&#x00E7;&#x00E3;o para S&#x00E3;o Paulo necessita ser revista. A presen&#x00E7;a dessas esp&#x00E9;cies mostra a import&#x00E2;ncia de se conservar e cuidar desse remanescente florestal.</p>
+        </sec>
+        <sec sec-type="conclusions">
+            <title>Conclus&#x00F5;es</title>
+            <p>Dentre as conclus&#x00F5;es deste estudo, podemos constatar que as tr&#x00EA;s &#x00E1;reas analisadas s&#x00E3;o floristicamente e estruturalmente diferentes, pois algumas das esp&#x00E9;cies amostradas est&#x00E3;o presentes em todas as &#x00E1;reas e outras s&#x00E3;o exclusivas em apenas uma ou duas delas e mesmo quando presentes nas tr&#x00EA;s &#x00E1;reas, n&#x00E3;o apresentam o mesmo VI em cada uma delas.</p>
+            <p>Todos os grupos sucessionais (pioneiras, secund&#x00E1;rias iniciais e tardias e umbr&#x00F3;filas) est&#x00E3;o presentes nas tr&#x00EA;s &#x00E1;reas, por&#x00E9;m em propor&#x00E7;&#x00F5;es distintas e tamb&#x00E9;m predominando variadamente em cada um de seus estratos.</p>
+            <p>Na &#x00E1;rea A, em seu dossel, h&#x00E1; predomin&#x00E2;ncia de esp&#x00E9;cies secund&#x00E1;rias tardias; estrato m&#x00E9;dio com secund&#x00E1;rias iniciais e o sub-bosque, majoritariamente, formado por esp&#x00E9;cies umbr&#x00F3;filas. Esta &#x00E1;rea ainda contem baixa representatividade de esp&#x00E9;cies pioneiras e secund&#x00E1;rias iniciais que ocorrem em pequenas clareiras e bordas da mancha estudada.</p>
+            <p>Na &#x00E1;rea B, as esp&#x00E9;cies secund&#x00E1;rias iniciais predominam tanto no dossel quanto no estrato m&#x00E9;dio da floresta e o sub-bosque &#x00E9; formado por todos os grupos sucessionais, exceto as pioneiras, estas com baixa representatividade e, quando presentes, est&#x00E3;o restritas a pequenas clareiras, o mesmo que ocorre na &#x00E1;rea A.</p>
+            <table-wrap-group id="t4">
+                <table-wrap xml:lang="pt">
+                    <label>Tabela 4</label>
+                    <caption>
+                        <title>Lista de esp&#x00E9;cies amea&#x00E7;adas e sua classifica&#x00E7;&#x00E3;o nas listas de <xref ref-type="bibr" rid="B48">S&#x00E3;o Paulo (2016)</xref>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulner&#x00E1;vel, EN: Em perigo e EX: Extinta.</title>
+                    </caption>
+                </table-wrap>
+                <table-wrap xml:lang="en">
+                    <label>Table 4</label>
+                    <caption>
+                        <title>List of threatened species and their classification in the lists of <xref ref-type="bibr" rid="B48">S&#x00E3;o Paulo, 2016</xref>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.</title>
+                    </caption>
+                    <table>
+                        <thead>
+                            <tr>
+                                <th rowspan="2" align="left">Esp&#x00E9;cie</th>
+                                <th align="left"/>
+                                <th align="center">Listas</th>
+                                <th align="left"/>
+                            </tr>
+                            <tr>
+                                <th align="center">S&#x00E3;o Paulo</th>
+                                <th align="center">Brasil</th>
+                                <th align="center">IUCN</th>
+                            </tr>
+                        </thead>
+                        <tbody>
+                            <tr>
+                                <td align="left"><italic>Ocotea catharinensis</italic> Mez</td>
+                                <td align="center">VU</td>
+                                <td align="center">VU</td>
+                                <td align="center">VU</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Cedrela fissilis</italic> Vell.</td>
+                                <td align="center">VU</td>
+                                <td align="center">VU</td>
+                                <td align="center">EN</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Trichilia silvatica</italic> C.DC.</td>
+                                <td align="center">-</td>
+                                <td align="center">-</td>
+                                <td align="center">VU</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Virola bicuhyba</italic> (Schott ex Spreng.) Warb.</td>
+                                <td align="center">EN</td>
+                                <td align="center">EN</td>
+                                <td align="center">-</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Eugenia prasina</italic> O.Berg</td>
+                                <td align="center">-</td>
+                                <td align="center">-</td>
+                                <td align="center">VU</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Euplassa cantareirae</italic> Sleumer</td>
+                                <td align="center">EX</td>
+                                <td align="center">EN</td>
+                                <td align="center">-</td>
+                            </tr>
+                            <tr>
+                                <td align="left"><italic>Pouteria bullata</italic> (S.Moore) Baehni</td>
+                                <td align="center">EN</td>
+                                <td align="center">EN</td>
+                                <td align="center">VU</td>
+                            </tr>
+                        </tbody>
+                    </table>
+                </table-wrap>
+            </table-wrap-group>
+            <p>A &#x00E1;rea C possui dossel descont&#x00ED;nuo com predom&#x00ED;nio de pioneiras; o estrato m&#x00E9;dio apresenta predom&#x00ED;nio de pioneiras e iniciais, mas com poucas tardias e umbr&#x00F3;filas. As clareiras dessa &#x00E1;rea s&#x00E3;o maiores que em A e B. As esp&#x00E9;cies pioneiras comp&#x00F5;em o dossel desta floresta.</p>
+            <p>Conclui-se, pela an&#x00E1;lise, que a &#x00E1;rea A est&#x00E1; em processo de sucess&#x00E3;o mais avan&#x00E7;ado ou final, a &#x00E1;rea B em fase intermedi&#x00E1;ria e, a C, em uma fase mais inicial das anteriores.</p>
+            <p>Avaliar o est&#x00E1;gio successional de uma determinada &#x00E1;rea &#x00E9; um grande desafio cient&#x00ED;fico, com importantes implica&#x00E7;&#x00F5;es na conserva&#x00E7;&#x00E3;o. Conhecer a floresta em diferentes est&#x00E1;gios traz subs&#x00ED;dios a medidas aplicadas visando a recupera&#x00E7;&#x00E3;o, n&#x00E3;o somente do Parque Estadual da Cantareira, como da Serra da Cantareira e demais &#x00E1;reas da Floresta Ombr&#x00F3;fila Densa Montana. A floresta do Parque Estadual da Cantareira, especificamente no N&#x00FA;cleo Pedra Grande, apesar de haver sofrido grande press&#x00E3;o antr&#x00F3;pica, ainda abriga remanescentes florestais preservados, dos quais a &#x00E1;rea A &#x00E9; um exemplo, que servem como fonte de sementes e outras unidades de dispers&#x00E3;o para a recupera&#x00E7;&#x00E3;o natural dos trechos em est&#x00E1;gio sucessional em fases intermedi&#x00E1;ria a inicial, como as &#x00E1;reas B e C do presente estudo.</p>
+            <p>Estudos de recupera&#x00E7;&#x00E3;o natural da vegeta&#x00E7;&#x00E3;o nativa em florestas do Planalto Paulista al&#x00E9;m de serem escassos, s&#x00E3;o de grande import&#x00E2;ncia para garantir &#x00E0;s gera&#x00E7;&#x00F5;es futuras a manuten&#x00E7;&#x00E3;o dos servi&#x00E7;os ecossist&#x00EA;micos da Floresta Ombr&#x00F3;fila Densa, a Mata Atl&#x00E2;ntica, hoje ainda bastante afetada pela fragmenta&#x00E7;&#x00E3;o e consequente perda de biodiversidade.</p>
+        </sec>
+    </body>
+    <back>
+        <ack>
+            <title>Agradecimentos</title>
+            <p>Agradecemos ao Conselho Nacional de Desenvolvimento Cient&#x00ED;fico e Tecnol&#x00F3;gico, pela Bolsa de Mestrado concedida &#x00E0; primeira Autora (Processo n&#x00BA; 133843/2018-9) junto ao Programa de P&#x00F3;s-Gradua&#x00E7;&#x00E3;o em Biodiversidade Vegetal e Meio Ambiente do Instituto de Bot&#x00E2;nica de S&#x00E3;o Paulo.</p>
+        </ack>
+        <ref-list>
+            <title>Literatura Citada</title>
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+                    <source>Biota Neotropica</source>
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+                    <year>1998</year>
+                    <source>A Reserva da Biosfera da Mata Atl&#x00E2;ntica e sua aplica&#x00E7;&#x00E3;o no Estado de S&#x00E3;o Paulo: apresenta&#x00E7;&#x00E3;o Covas, M.; pref&#x00E1;cio Feldmann, F. J</source>
+                    <publisher-loc>S&#x00E3;o Paulo</publisher-loc>
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+                <mixed-citation>S&#x00E3;o Paulo. 2016. Resolu&#x00E7;&#x00E3;o SMA n&#x00BA; 057, de 05 de junho de 2016. Publica a segunda revis&#x00E3;o da lista oficial das esp&#x00E9;cies da flora amea&#x00E7;adas de extin&#x00E7;&#x00E3;o no Estado de S&#x00E3;o Paulo. Di&#x00E1;rio Oficial do Estado de S&#x00E3;o Paulo, de 30/06/2016, Se&#x00E7;&#x00E3;o 1, pp. 55-57.</mixed-citation>
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diff --git a/tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/expected.html b/tests/fixtures/table_wrap_group_and_fig_group/2236-8906-hoehnea-49-e1082020/expected.html
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+<html class="no-js">
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+<meta http-equiv="X-UA-Compatible" content="IE=edge,chrome=1">
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+<span class="_articleBadge">Artigo</span><span class="_separator"> • </span><span class="_editionMeta">Hoehnea 49 <span class="_separator"> • </span>2022</span><span class="_separator"> • </span><span class="group-doi"><a href="https://doi.org/10.1590/2236-8906-108/2020" class="_doi" target="_blank">https://doi.org/10.1590/2236-8906-108/2020</a>
+         
+        <a class="copyLink" data-clipboard-text="https://doi.org/10.1590/2236-8906-108/2020"><span class="sci-ico-link"></span>copiar</a></span>
+</div>
+<h1 class="article-title">
+<span class="sci-ico-openAccess showTooltip" data-toggle="tooltip" data-original-title="by 4.0 "></span>Florestas secundárias do Parque Estadual da Cantareira, São Paulo, SP, Brasil: Variações florísticas e estruturais<span class="ref footnote"><sup class="xref">1</sup><span class="refCtt closed"><span class="refCttPadding"><strong class="fn-title">1</strong>Parte da Dissertação de Mestrado do primeiro Autor</span></span></span><a id="shorten" href="#" class="short-link"><span class="sci-ico-link"></span></a>
+</h1>
+<h2 class="article-title">Secondary forests of the Parque Estadual da Cantareira, São Paulo State, SP, Brasil: Floristic and structural variations</h2>
+<div class="articleMeta"></div>
+<div class="contribGroup">
+<span class="dropdown"><a id="contribGroupTutor1" class="dropdown-toggle" data-toggle="dropdown"><span> Rafaela Dias Valeck da Silva </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor1">
+<strong></strong>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil<div class="corresp">4 Autora para correspondência: <a href="mailto:rafaela_valeck@hotmail.com">rafaela_valeck@hotmail.com</a>
+</div>
+<a href="http://orcid.org/0000-0002-9049-3704" class="btnContribLinks orcid">http://orcid.org/0000-0002-9049-3704</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor2" class="dropdown-toggle" data-toggle="dropdown"><span> Inês Cordeiro </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor2">
+<strong></strong>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil<a href="http://orcid.org/0000-0002-2626-5280" class="btnContribLinks orcid">http://orcid.org/0000-0002-2626-5280</a>
+</ul></span><span class="dropdown"><a id="contribGroupTutor3" class="dropdown-toggle" data-toggle="dropdown"><span> Frederico Alexandre Roccia Dal Pozzo Arzolla </span></a><ul class="dropdown-menu" role="menu" aria-labelledby="contribGrupoTutor3">
+<strong></strong>Instituto Florestal, Rua do Horto, 931, 02377-000 São Paulo, SP, Brasil<a href="http://orcid.org/0000-0003-3111-6877" class="btnContribLinks orcid">http://orcid.org/0000-0003-3111-6877</a>
+</ul></span><a href="" class="outlineFadeLink" data-toggle="modal" data-target="#ModalTutors">Sobre os autores</a>
+</div>
+<div class="row">
+<ul class="col-md-2 hidden-sm articleMenu"></ul>
+<article id="articleText" class="col-md-10 col-md-offset-2 col-sm-12 col-sm-offset-0"><div class="articleSection" data-anchor="RESUMO">
+<h1 class="articleSectionTitle">RESUMO</h1>
+<p>O Parque Estadual da Cantareira, no bioma da Mata Atlântica, foi criado a partir da desapropriação de fazendas de café para proteção de mananciais para a cidade de São Paulo em 1877. Desde então, poucas atividades humanas ocorreram em seu interior. Aqui, comparamos a composição e o estágio sucessional de diferentes fragmentos de floresta próximos (&lt;0,5 km um do outro). Foram levantados 0,6 ha, divididos em três áreas de 0,2 ha cada, com árvores atingindo PAP ≥ 15 cm, sendo amostradas, identificadas e medidos o diâmetro e a altura. O estágio sucessional das espécies foi determinado e um perfil de cada área foi desenhado em escala. Um total de 1.020 indivíduos pertencentes a 45 famílias e 115 espécies foi amostrado. Os fragmentos variaram em número de indivíduos (300-399 indivíduos), famílias (N = 26-32) e espécies (N = 54-68), altura e estágios sucessionais, indicando alta heterogeneidade dentro de uma floresta contínua, desde os estágios sucessionais maduros até os iniciais. Essas descobertas têm implicações para o manejo da conservação e os serviços ecossistêmicos fornecidos por eles.</p>
+<p><strong>Palavras-chave:</strong><br>Fitossociologia; Mata Atlântica; sucessão</p>
+</div>
+<div class="articleSection" data-anchor="ABSTRACT">
+<h1 class="articleSectionTitle">ABSTRACT</h1>
+<p>The Parque Estadual da Cantareira, in the Atlantic Forest biome, was created from the expropriation of coffee farms for the protection of water sources for São Paulo city in 1877. Since then, few human activities have taken place in its interior. Here, we compare the composition and the successional stages of different fragments of near forests (&lt;0.5 km of each other); 0.6 ha were raised, divided in three areas of 0.2 ha each, with trees reaching PAP ≥ 15 cm, being sampled, identified and measured for diameter and height. The succession stage of the species was determined and a profile of each area was drawn in scale. A total of 1,020 individuals of 45 families and 115 species was sampled. The fragments varies in number of in individuals (300-399 individuals), families (N = 26-32) and species (N = 54-68), height and successional stages, indicating high heterogeneity within a continuous forest, from the mature successional stages to the first ones. These discoveries have implications for conservation management and the ecosystem service they provide.</p>
+<p><strong>Keywords:</strong><br>Atlantic Rainforest; Phytosociology; succession</p>
+</div>
+<div class="articleSection" data-anchor="Text">
+<h1 class="articleSectionTitle">Introdução</h1>
+<p>A Mata Atlântica ocupa aproximadamente 15% do território brasileiro sendo considerada mundialmente o 5º bioma mais ameaçado (<span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>). Estende-se desde o Piauí até o Estado do Rio Grande do Sul, englobando assim 17 Estados brasileiros (<span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>). A ampla variação de temperatura, relevo e solo ao longo da Mata Atlântica, fazem desta uma das florestas de maior biodiversidade do mundo (<span class="ref"><strong class="xref xrefblue">Leitão-Filho 1987</strong><span class="refCtt closed"><span>Leitão-Filho, H.F. 1987. Considerações sobre a florística de florestas tropicais e sub-tropicais do Brasil. IPEF 45: 41-46.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Lino &amp; Amaral 2018</strong><span class="refCtt closed"><span>Lino, C.F. &amp; Amaral, M.M. 2018. Mata Atlântica e Sociobiodiversidade: Desafios e caminhos para a sustentabilidade. CN-RBMA Conselho Nacional da Reserva da Biosfera da Mata Atlântica. São Paulo: IA- RBMA.</span></span></span>). Pelo alto número de espécies endêmicas e forte pressão antrópica, o Bioma Mata Atlântica, juntamente com o Cerrado, é considerado um dos hostspots do planeta (<span class="ref"><strong class="xref xrefblue">Myers <i>et al</i>. 2000</strong><span class="refCtt closed"><span>Myers, N., Mittermeier, R.A., Mittermeier, C.G., Fonseca, G.A.B. 2000. Kent, J. Biodiversity hotspots for conservation priorities. Nature 403: 853-845.</span></span></span>)</p>
+<p>A Mata Atlântica é composta pelas seguintes formações vegetais: Floresta Ombrófila Densa, Aberta e Mista (conhecida como Floresta de Araucárias); Floresta Estacional Semidecidual e Decidual; Campos de Altitude; Manguezais, Restingas, Campos Salinos e Áreas Aluviais; Áreas de Tensão Ecológica; Refúgios Vegetacionais (<span class="ref"><strong class="xref xrefblue">IBGE 2019</strong><span class="refCtt closed"><span>IBGE. Fundação Instituto Brasileiro de Geografia e Estatística. Disponível em http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html (acesso em 16-XI-2019).</span><br><a href="http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html" target="_blank">http://7a12.ibge.gov.br/vamos-conhecer-o...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Fundação SOS Mata Atlântica 2020</strong><span class="refCtt closed"><span>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).</span><br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">http://aquitemmata.org.br/#/busca/sp/S%C...
+            </a></span></span>).</p>
+<p>As Florestas Ombrófilas Densas se subdividem em 5 grupos principais: Floresta Ombrófila Densa de Terras Baixas, presente até 50 metros de altitude; Floresta Ombrófila Densa Submontana, 50 a 500 metros; Floresta Ombrófila Densa Montana, 500 a 1500 metros e a Floresta Ombrófila Densa Altomontana, acima de 1500 metros, e a Floresta Ombrófila Densa Aluvial, presente em qualquer das formações anteriores, ao longo dos cursos d’água (<span class="ref"><strong class="xref xrefblue">IBGE 2012</strong><span class="refCtt closed"><span>IBGE. 2012. Fundação Instituto Brasileiro de geografia e Estatística. Manual técnico da vegetação brasileira. 2ed, Rio de Janeiro.</span></span></span>).</p>
+<p>No Estado de São Paulo, a diminuição drástica da cobertura florestal deveu-se a fatores antrópicos, principalmente o estabelecimento de culturas, inicialmente a do café e o adensamento populacional nos núcleos urbanos (<span class="ref"><strong class="xref xrefblue">Rocha &amp; Costa 1998</strong><span class="refCtt closed"><span>Rocha, A.A. &amp; Costa, J.P.O. 1998. A Reserva da Biosfera da Mata Atlântica e sua aplicação no Estado de São Paulo: apresentação Covas, M.; prefácio Feldmann, F. J. - São Paulo: Terra Virgem, Secretaria do Meio Ambiente do Estado de São Paulo.</span></span></span>, RBMA 2019).</p>
+<p>Apesar da destruição da floresta ao longo da história de São Paulo, o Estado ainda preserva a maior área contínua da Mata Atlântica no Brasil, nas encostas da Serra do Mar (<span class="ref"><strong class="xref xrefblue">Leite 2007</strong><span class="refCtt closed"><span>Leite, M. 2007. Nos caminhos da Biodiversidade Paulista / Nas Costas do Brasil. Os litorais paulistas. São Paulo: Secretaria do Meio Ambiente: Instituto Amigos da Reserva da Biosfera da Mata Atlântica: Imprensa oficial do Estado de São Paulo.</span></span></span>). Alguns trabalhos mais recentes relatam o aumento da cobertura florestal, representada por florestas secundárias em diferentes estágios de regeneração (<span class="ref"><strong class="xref xrefblue">Farinaci &amp; Batistella 2012</strong><span class="refCtt closed"><span>Farinaci, J.S. &amp; Batistella, E.M. 2012. Variação na cobertura vegetal nativa em São Paulo: Um panorama do conhecimento atual. Revista Árvore 36(4): 695-705, 2012.</span></span></span>).</p>
+<p>O que resta da Mata Atlântica está inserido em 1.324 Unidades de Conservação (UCs). As Unidades de Conservação possuem uma classificação própria, pois a diversidade do ambiente resulta em objetivos e manejos distintos.</p>
+<p>A sucessão é o processo natural de desenvolvimento da comunidade vegetal que possibilita o estabelecimento de plantas em uma área desprovida de vegetação ou a regeneração da vegetação onde esta sofreu algum tipo de distúrbio (<span class="ref"><strong class="xref xrefblue">Brancalion <i>et al.</i> 2015</strong><span class="refCtt closed"><span>Brancalion, H.S., Galdolfi, S., Rodrigues, R. R. 2015. Restauração Florestal. Oficina de Textos, São Paulo.</span></span></span>).</p>
+<p>Para cada fase da sucessão, em uma floresta secundária, há predomínio de determinadas espécies pertencentes a um grupo sucessional (<span class="ref"><strong class="xref xrefblue">Clements 1916</strong><span class="refCtt closed"><span>Clements, F.E. 1916. Plant succession: Na analysis of the development of vegetation. BHL: Biodiversity Heritage Library. Disponível em www.biodversitylibrary.org/ (acesso em 18-V-2020).</span><br><a href="www.biodversitylibrary.org/" target="_blank">www.biodversitylibrary.org/...
+            </a></span></span>). Segundo <span class="ref"><strong class="xref xrefblue">Whitmore (1989)</strong><span class="refCtt closed"><span>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</span></span></span>, o conhecimento sobre a substituição de espécies ao longo do processo de sucessão, é fundamental para avaliar o grau de maturidade em que se encontra um determinado fragmento florestal.</p>
+<p>Conforme a <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>tabela 1</a>, o primeiro estudo a classificar as espécies por suas respectivas categorias foi realizado por <span class="ref"><strong class="xref xrefblue">Budowski (1965)</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span>, este utilizou as categorias pioneira, secundária inicial, secundária tardia e clímax. Posteriormente, alguns autores classificaram as espécies de forma mais sucinta, ou seja, espécies pioneiras e não-pioneiras como: <span class="ref"><strong class="xref xrefblue">Gómez-Pompa (1971)</strong><span class="refCtt closed"><span>Gómez-Pompa, A. 1971. Posible papel de la vegetación secundaria en la evolución de la flora tropical. Biotropica 3: 125-135.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Whitmore (1989)</strong><span class="refCtt closed"><span>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>. Já, em outros estudos, os autores optaram por classificar as espécies separando as não pioneiras, por secundárias iniciais e secundárias tardias e as espécies típicas de sub-bosque ou conhecidas como umbrófilas.</p>
+<p>Portanto, conforme as análises dos estudos apresentados na <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet1"><span class="sci-ico-fileTable"></span>tabela 1</a>, as espécies pioneiras predominam no início da sucessão, podem ser encontradas em grandes clareiras, produzem sementes pequenas e abundantes, que necessitam de luz direta para germinar, além disso tem crescimento rápido e ciclo de vida curto; as espécies secundárias iniciais estabelecem-se em pequenas clareiras, assemelham-se às pioneiras quanto à necessidade de luz para germinar suas sementes, mas têm ciclo de vida mais longo; as secundárias tardias destacam-se na fase mais madura da floresta, suas sementes não necessitam de luz direta para germinar e são geralmente maiores, menos abundantes que as das espécies pioneiras, podem apresentar dormência e suas plântulas vivem na sombra, com crescimento lento e ciclo de vida longo; as espécies umbrófilas ou típicas de sub-bosque, estão presentes em todas as fases, mas com maior densidade na fase madura. O que as diferem das secundárias tardias é que em todo seu ciclo de vida se desenvolvem inteiramente no estrato inferior da floresta (<span class="ref"><strong class="xref xrefblue">Budowski 1965</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gómez-Pompa 1971</strong><span class="refCtt closed"><span>Gómez-Pompa, A. 1971. Posible papel de la vegetación secundaria en la evolución de la flora tropical. Biotropica 3: 125-135.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Swaine &amp; Whitmore 1988</strong><span class="refCtt closed"><span>Swaine, M.D. &amp; Whitmore, T.C. 1988. On the definition of ecological species groups in tropical rain forests. Vegetation 75: 81-86.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Kageyama &amp; Castro 1989</strong><span class="refCtt closed"><span>Kageyama, P.Y. &amp; Castro, C.F.A. 1989. Sucessão secundária, Estrutura genética e Plantações de espécies arbóreas nativas. Instituto de Pesquisas e Estudos Florestais 41/42: 83-93.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Gandolfi 1991</strong><span class="refCtt closed"><span>Gandolfi, F. 1991. Estudo florístico e fitossociológico de uma floresta residual na área do Aeroporto Internacional de São Paulo, Município de Guarulhos, SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. 2006</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>).</p>
+<p>No Estado de São Paulo, uma importante unidade de conservação é o Parque Estadual da Cantareira, localizado na região metropolitana da cidade de São Paulo, sendo um dos principais remanescentes florestais, formados por florestas secundárias em diferentes estágios sucessionais, porém mantendo alta riqueza de biodiversidade.</p>
+<p>Estudos sobre a dinâmica do processo sucessional em florestas do Planalto Paulista são escassos. Portanto, o presente estudo poderá fornecer contribuições para a temática e para aplicações práticas no âmbito local e regional.</p>
+<p>O objetivo deste estudo foi comparar quanto ao estágio sucessional, trechos da floresta do Parque Estadual da Cantareira através da análise de sua estrutura e espécies características de seus estratos, contribuindo para o conhecimento, conservação e a proteção das florestas secundárias urbanas.</p>
+<p>Para tanto elaboramos as seguintes perguntas:</p>
+<p>A. Como a composição florística e a estrutura variam nas áreas analisadas?</p>
+<p>B. É possível reconhecer estágios sucessionais diferentes nas áreas estudadas?</p>
+<p>C. Como as espécies de diferentes grupos sucessionais estão representadas nas áreas estudadas?</p>
+<h1 class="articleSectionTitle">Material e Métodos</h1>
+<p>Área de Estudo - O Parque Estadual da Cantareira (PEC) possui 7.916,5 hectares, abrangendo parte dos munícipios de Caieiras, Guarulhos, Mairiporã e São Paulo, na bacia do Alto Tietê, na Serra da Cantareira. Destaca-se entre seus serviços ecossistêmicos, a grande riqueza de mananciais que abriga em sua área (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>Essa região anteriormente é composta por fazendas de café, que foram adquiridas pelo governo do Estado, preocupado com o abastecimento de água. A captação de água na Serra da Cantareira iniciou-se em 1877. O abastecimento acontecia a partir de um sistema de pequenas represas, suficientes para abastecer a população que residia no centro da cidade com uma água de excelente qualidade. Com o aumento da urbanização, os mananciais da Serra da Cantareira deixaram de ser suficientes para o abastecimento da cidade de São Paulo. Atualmente, apenas uma parte do município de Guarulhos é abastecida pelos mananciais do PEC (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>Como resultado deste histórico, formou-se uma floresta secundária, onde predominam manchas em fases intermediárias de sucessão (<span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. 1993</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>O PEC é composto por 4 zonas administrativas: Núcleo Engordador, localizado entre os municípios de Mairiporã e São Paulo; Águas Claras, no município de Mairiporã; Cabuçu em Guarulhos e Pedra Grande, que abrange parte dos municípios de Caieiras, Mairiporã e São Paulo (<span class="ref"><strong class="xref xrefblue">Ayres 2006</strong><span class="refCtt closed"><span>Ayres, N.C.M. 2006. O ciclo da Caapora: Uma história de relação entre a RMSP e o Parque Estadual da Cantareira (1963 - 2005). São Paulo. Dissertação de Mestrado, Universidade Católica de São Paulo. São Paulo.</span></span></span>, <span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<p>A área de estudo está localizada no Núcleo Pedra Grande. Conforme o <span class="ref"><strong class="xref xrefblue">IBGE (2012)</strong><span class="refCtt closed"><span>IBGE. 2012. Fundação Instituto Brasileiro de geografia e Estatística. Manual técnico da vegetação brasileira. 2ed, Rio de Janeiro.</span></span></span>, a área é recoberta pela Floresta Ombrófila Densa Montana. De acordo com a classificação de Köppen, o clima é do tipo úmido, temperado e sem estação seca - Cfb (<span class="ref"><strong class="xref xrefblue">São Paulo 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>), ou seja, com precipitação média do mês mais seco &gt; 30 mm e a temperatura média do mês mais quente &lt;22ºC (<span class="ref"><strong class="xref xrefblue">Köppen 2019</strong><span class="refCtt closed"><span>Köppen, G. Classificação Climática de Koppen-Geiser. Disponível em https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf (acesso em 17-XI-2019).</span><br><a href="https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf" target="_blank">https://portais.ufg.br/up/68/o/Classific...
+            </a></span></span>). O relevo é montanhoso, com amplitudes de 120 a 400 metros e altitudes de 875 a 1215 metros (<span class="ref"><strong class="xref xrefblue">São Paulo, 2010</strong><span class="refCtt closed"><span>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</span></span></span>).</p>
+<div class="row table" id="t1">
+<a name="t1"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 1</strong></strong><br> Classificação Sucessional adotada por alguns autores ao longo dos anos.<br><strong><strong>Table 1</strong></strong><br> Sucessional classification adopted by some authors over the years.<br>
+</div>
+</div>
+<p>Métodos - Para o presente estudo foram selecionadas três áreas amostrais de 0,2 ha cada, subdivididas em dez parcelas contíguas de 10 x 20 m, totalizando uma área amostral de 0,6 ha. A distância aproximada entre a área C e A é de 250 m e da área A para B de 400 m, com as respectivas localizações: área A (23°25’46”S, 46°38’6”O), área B (23°25’40”S, 46°37’54”O) e área C (23°25’53”S, 46°38’0”O) (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf1"><span class="sci-ico-fileFigure"></span>figura 1</a>). As três áreas encontram-se afastadas das trilhas para se evitar o efeito de borda, como recomendado por <span class="ref"><strong class="xref xrefblue">Rodrigues &amp; Shepherd (1992)</strong><span class="refCtt closed"><span>Rodrigues, R.R. &amp; Shepherd, G.J. 1992. Análise da variação estrutural e fisionômica da vegetação e características edáficas, num gradiente altitudinal na Serra do Japi. In: L.P.C. Morellato (org.). História natural da Serra do Japi: ecologia e preservação de uma área florestal no sudeste do Brasil. Editora Unicamp: Campinas, pp. 64-96.</span></span></span> e possuem declividades semelhantes.</p>
+<p>Foram amostrados todos os indivíduos com PAP, perímetro do tronco à altura de 1,30 m acima do solo ≥ 15 cm. Os indivíduos mortos, mesmo em pé, não foram amostrados. A altura das árvores foi estimada utilizando-se tesoura de poda alta como referência. As amostras botânicas foram coletadas, herborizadas e identificadas por comparação com exsicatas depositadas em herbário, consultas a especialistas e bibliografias específicas. As amostras férteis foram registradas e incorporadas no Herbário Dom Bento Pickel (SPSF) do Instituto Florestal.</p>
+<p>Para a classificação das famílias, foi utilizado o Angiosperm Phylogeny Group - APG IV (<span class="ref"><strong class="xref xrefblue">APG - Angiosperm Phylogeny Group 2016</strong><span class="refCtt closed"><span>APG - Angiosperm Phylogeny Group. 2016. An update of the Angiosperm Phylogeny Group Classification for the orders and families of flowering plants: APG IV. Botanical Journal of the Linnean Society 181: 1-20.</span></span></span>). Os nomes científicos foram conferidos com a lista de espécies da Flora do Brasil (<span class="ref"><strong class="xref xrefblue">Flora do Brasil 2020 - em construção 2020</strong><span class="refCtt closed"><span>Flora do Brasil 2020 em construção. Jardim Botânico do Rio de Janeiro. Disponível em (http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964) (acesso em 11-III-2020).</span><br><a href="http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964" target="_blank">http://floradobrasil.jbrj.gov.br/reflora...
+            </a></span></span>).</p>
+<p>Os parâmetros fitossociológicos calculados nas análises foram: número de indivíduos (ni), densidade relativa (DR), dominância relativa (DoR), frequência relativa (FR), valor de cobertura (VC) e valor de importância (VI), segundo <span class="ref"><strong class="xref xrefblue">Mueller-Dombois &amp; Ellenberg (1974)</strong><span class="refCtt closed"><span>Mueller-Dombois, D. &amp; Ellenberg, H. 1974. Aims and methods of vegetation ecology. New York: John Wiley &amp; Sons.</span></span></span>. Também foram realizadas análises multivariadas de classificação e ordenação, utilizando-se matrizes de número de indivíduos, para verificar a eventual formação de grupos nas unidades amostrais da área de estudo e comparar as parcelas e blocos entre si. Nas análises de classificação, para comparação de matrizes de números de indivíduos, foram utilizados os métodos UPGMA - Unweighted Pair Group Method with Arithmetic Mean com coeficiente de Bray-Curtis. Como método de ordenação foi utilizado CA (Análise de Correspondência). Para esses cálculos e análises, foi utilizado o programa Fitopac 2.1 (<span class="ref"><strong class="xref xrefblue">Shepherd 2010</strong><span class="refCtt closed"><span>Shepherd, G. J. 2010. Fitopac 2.1. Manual do usuário. Campinas: UNICAMP.</span></span></span>).</p>
+<p>As espécies foram classificadas segundo o tipo de dispersão de seus propágulos, como zoocóricas, anemocóricas e autocóricas, de acordo com <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>); <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>.</p>
+<p>A apresentação das espécies ameaçadas deu-se pelas consultas às seguintes listas: IUCN (2020), nacional (Portaria MMA nº 443, de 17 de dezembro de 2014 - Brasil 2020) e estadual (Resolução SMA Nº 57, de 05 de junho de 2016 - <span class="ref"><strong class="xref xrefblue">São Paulo 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>).</p>
+<p>A classificação das espécies, segundo a categoria sucessional, foi baseada, principalmente, em observações de campo e em trabalhos realizados por <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>. Foram feitas duas classificações sucessionais, uma com quatro categorias: pioneiras, secundárias iniciais, secundárias tardias e umbrófilas, sendo as três primeiras conforme <span class="ref"><strong class="xref xrefblue">Budowski (1965)</strong><span class="refCtt closed"><span>Budowski, G. 1965. Distribution of tropical rain forest species in the light of sucessional processes. Turrialba 15(1): 40-42.</span></span></span> e, as umbrófilas, segundo <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span> e <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>; a segunda considerou as espécies como pioneiras e não-pioneiras (Secundárias iniciais, tardias e umbrófilas), adaptado de <span class="ref"><strong class="xref xrefblue">Barbosa (2017)</strong><span class="refCtt closed"><span>Barbosa, L.M. 2017. Lista de espécies indicadas para restauração ecológica para diversas regiões do Estado de São Paulo. Relatório Técnico, Secretaria do Meio Ambiente de São Paulo.</span></span></span>.</p>
+<p>Para auxiliar uma análise da distribuição das espécies em categoria sucessional, foram idealizados perfis diagramas totais de cada uma das áreas estudadas, com a representação dos indivíduos amostrados seguindo-se a sequência da planilha de campo, com núcleos diferentes segundo sua classificação sucessional.</p>
+<h1 class="articleSectionTitle">Resultados</h1>
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+<strong>Figura 1</strong><br>Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.<br><strong>Figure 1</strong><br>Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.<br>
+</div>
+</div>
+<p>Composição Florística - No levantamento geral, foram amostrados 1020 indivíduos, distribuídos em 115 espécies, 80 gêneros e 45 famílias (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet2"><span class="sci-ico-fileTable"></span>tabela 2</a>). A área B é mais rica, com 68 espécies, sendo 21% mais rica que C (56 spp.) e 26% mais rica que A (54 spp.).</p>
+<p>As famílias mais ricas em espécies foram Myrtaceae (17 espécies), Lauraceae (12), Fabaceae (8), Rubiaceae e Meliaceae (5). As famílias mais abundantes em indivíduos foram Euphorbiaceae (127 indivíduos), Myrtaceae (115), Olacaceae (114), Rubiaceae (108) e Meliaceae (68).</p>
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+<strong><strong>Tabela 2</strong></strong><br> Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.<br><strong><strong>Table 2</strong></strong><br> Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.<br>
+</div>
+</div>
+<p>Os gêneros mais ricos foram <i>Eugenia, Myrcia</i> e <i>Ocotea</i> (sete espécies cada), <i>Mollinedia</i> (quatro) e <i>Annona</i> e <i>Casearia</i> (três cada).</p>
+<p>Riqueza e Abundância nas Áreas A, B e C - Na Área A foram amostrados 321 indivíduos, 54 espécies e 26 famílias. As famílias com maior riqueza foram Myrtaceae (10 espécies), Lauraceae (6 esp.), Euphorbiaceae e Rubiaceae (4 esp.) e Monimiaceae (3 esp.). As famílias mais abundantes foram Rubiaceae (70 indivíduos), Olacaceae (42 ind.), Myrtaceae (32 ind.), Clusiaceae (23 ind.) e Monimiaceae (20 ind.). As famílias Rubiaceae e Olacaceae destacam-se nas primeiras posições quanto à abundância, não ocorrendo o mesmo em relação a riqueza, mostrando que a alta abundância dessas famílias é por causa de uma espécie, <i>Psychotria suterella</i> em Rubiaceae e <i>Heisteria silvianii</i> em Olacaceae. Os gêneros mais ricos foram <i>Myrcia</i> (quatro espécies), <i>Eugenia, Ocotea</i> e <i>Mollinedia</i> (três cada), <i>Annona</i> e <i>Cinnamomum</i> (duas cada). Podemos observar que dentre estas, somente <i>Cinnamomum</i> não se destacou nos resultados gerais.</p>
+<p>A Área B apresentou 399 indivíduos, 68 espécies e 32 famílias. As famílias com maior riqueza foram Myrtaceae (10 espécies), Lauraceae (7 esp.), Meliaceae (5 esp.), Sapindaceae e Monimiaceae (4 esp.).</p>
+<p>As famílias mais abundantes em número de indivíduos foram Myrtaceae (72 indivíduos), Sapindaceae (39 ind.), Meliaceae (38 ind.), Olacaceae (37 ind.) e Rubiaceae (31 ind.). Nesta área, Sapindaceae e Meliaceae, destacaram-se tanto no levantamento por espécies quanto de indivíduos. Os gêneros que se destacaram nesta área foram <i>Eugenia</i> (cinco espécies), <i>Mollinedia, Myrcia</i> e <i>Ocotea</i> (quatro espécies cada), também amostradas na área A, seguidas de <i>Casearia</i> (três) e <i>Matayba</i> (duas). Área C apresentou 300 indivíduos pertencentes a 56 espécies e 30 famílias. As famílias mais ricas foram Fabaceae (7 espécies), Lauraceae (6 esp.), Euphorbiaceae e Myrtaceae (4 esp.) e Meliaceae (2 esp.). As famílias Fabaceae e Euphorbiaceae também foram as mais ricas no levantamento realizado na Floresta Ombrófila Densa situada no município de Cunha - SP por <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span>. As famílias mais abundantes foram Euphorbiaceae (94 ind.), Olacaceae (35 ind.), Fabaceae (32 ind.), Meliaceae (16 ind.) e Lauraceae (15 ind). Em relação aos gêneros, aqueles que mais se destacaram nesta análise foram <i>Annona, Croton, Mollinedia, Myrcia, Myrsine, Nectandra, Ocotea</i> e <i>Vochysia</i> (duas espécies cada), sendo que as quatro primeiras destacadas acima, apresentaram-se somente nesta área.</p>
+<p>Ao compararmos as três áreas de estudo, Olacaceae destaca-se pela abundância nas três áreas, entretanto Myrtaceae e Rubiaceae em duas delas. A alta representatividade de Olacaceae é devida a uma única espécie, <i>H. silvianii</i>, e Rubiaceae por <i>P. suterella</i>, enquanto que Myrtaceae, pela riqueza de espécies. Em relação aos gêneros que mais se destacaram nas áreas estudadas, podemos observar que a área C foi aquela mais distinta dentre elas, pois nesta área não há uma predominância de um gênero.</p>
+<p>Parâmetros fitossociológicos - A <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet3"><span class="sci-ico-fileTable"></span>tabela 3</a> mostra os parâmetros totais e por área, a área B apresentou 39% do número total de indivíduos amostrados, enquanto as áreas A e C, 31% e 30% respectivamente.</p>
+<p>Na área A, <i>H. silvianii</i> (22,7%), <i>Aspidosperma olivaceum</i> (18,1%) e <i>Euplassa cantareirae</i> (10,4%), espécies secundárias tardias, apresentaram os maiores valores de dominância relativa. As espécies que destacaram pelo valor de densidade foram <i>P. suterella</i> (19,6%), <i>H. silvianii</i> (13,1%) e <i>Tovomitopsis paniculata</i> (7,1%).</p>
+<p>Na área B, as espécies <i>Alchornea triplinervia</i> (22,6%), <i>H. silvianii</i> (11,1%), <i>Cabralea canjerana</i> (6,8%), <i>Casearia obliqua</i> (6,5%) e <i>Platymiscium floribundum</i> (6,4%) destacaram-se por seus valores de dominância relativa. Dentre elas, <i>H. silvianii</i> é a única secundária tardia e também apresentou alto valor de dominância na área A. Destacaram-se pelo valor de densidade, <i>H. silvianii</i> (9,3%), <i>Cupania oblongifolia</i> (8,8%), <i>Myrcia tijucensis</i> (7,3%) e <i>P. suterella</i> (7,0%).</p>
+<p>Na área C, destacaram-se pelo valor de dominância <i>Piptadenia gonoacantha</i> (26,50%), <i>Croton floribundus</i> (24,8%), <i>A. triplinervia</i> (10,4%) e <i>Bauhinia forficata</i> (6,8%). Destacaram-se pelo valor de densidade, <i>C. floribundus</i> (18,0%), <i>H. silvianii</i> (11,67%), <i>A. triplinervia</i> (7,7%) e <i>P. gonoacantha</i> (6,7%).</p>
+<p>Ao comparar as três áreas de estudo pelas espécies presentes, podemos constatar que as três áreas amostradas apresentam estrutura e composição florística distintas. Algumas espécies aparecem nas três áreas, mas em situações diferentes, por exemplo, <i>H. silvianii,</i> destacou-se tanto na área A e B, por seu valor de dominância, enquanto na área C, pela frequência, mostrando que nas duas primeiras áreas encontra-se no dossel, enquanto em C, nos estratos inferiores da floresta.</p>
+<p>Ao comparar a densidade das três áreas, constatamos que B (1995 ind./ha) é a mais densa, sendo 33% maior que C (1500 ind./ha) e 24% maior que A (1605 ind./ha). A maior densidade da área B pode ser explicada pelo predomínio de secundárias iniciais no dossel e pela grande quantidade de secundárias tardias no sub-bosque, estas últimas, em fase de crescimento, com um grande número de indivíduos jovens com pequenos diâmetros. Ao tratar-se de dominância, o cenário muda, pois, a área C apresenta a menor dominância (30,6 m<sup>2</sup> /ha), em comparação com as áreas A e B (45,4 m<sup>2</sup>/ha e 43,4 m<sup>2</sup>/ha, respectivamente), sendo 32,5% e 29,4% menor, respectivamente, enquanto os valores da área A e B são próximos.</p>
+<p>Os valores de DeA e DoA mostram que na área A, há vários indivíduos com grandes diâmetros, mas estes pertencem a um mesmo grupo ecológico (secundárias tardias), indicando que a área está mais avançada na sucessão. Na área B, as espécies com os maiores diâmetros pertencem a mais de um grupo ecológico, principalmente as secundárias iniciais e algumas tardias, devido à maior riqueza e ao maior número de indivíduos. Na área C, a situação é bem distinta, pois tanto a DeA quanto a DoA tem valores baixos, quando comparados com A e B, indicando um maior número de indivíduos com diâmetros menores.</p>
+<p>Análises grupos ecológicos - Na análise total de espécies, quanto aos seus respectivos grupos ecológico, as secundárias tardias e iniciais mantiveram-se em proporções próximas (33,9% e 29,6%, respectivamente), as umbrófilas com 20% e, as pioneiras, de menor riqueza de espécies, com 16,5%. Ao realizarmos as mesmas análises, com o número de indivíduos, os resultados permaneceram similares. Na análise por espécies pioneiras ou não-pioneiras, 46,1% são espécies pioneiras e 53,9% não-pioneiras e, analisando pelo número de indivíduos, 39,5% e 60,5% respectivamente, observando resultados diferentes.</p>
+<p>Na área A, as espécies secundárias tardias destacaram-se com 48,1% do total de espécies, seguidas das iniciais com 25,9%, umbrófilas com 22,2% e, por fim, as pioneiras com 3,7% (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf2"><span class="sci-ico-fileFigure"></span>figuras 2 a, b</a>). Nas mesmas análises com o número de indivíduos, o que se diferenciou foram as espécies umbrófilas, apresentando aumento de 13,7%, em função da riqueza da espécie <i>P. suterella</i>. E o oposto ocorreu com as iniciais, pois houve uma diminuição de 11,3%. Na análise de espécies classificadas como pioneiras ou não pioneiras, a porcentagem foi de 70,4% e 29,6%, respectivamente, enquanto abundância das espécies não-pioneiras foi 84,4% e pioneiras, 15,6%, do total de indivíduos amostrados. Esses resultados mostram que as espécies pertencentes ao grupo das pioneiras não são muito representadas pelo número de indivíduos.</p>
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+<strong><strong>Tabela 3</strong></strong><br> Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong><strong>Table 3</strong></strong><br> Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na área B, tanto as secundárias iniciais quanto as tardias apresentaram 35,3% do total de espécies, em seguida, as espécies umbrófilas com 22,1% e, as pioneiras, com 7,3%. Nas análises apresentadas pelo número de indivíduos não ocorreram grandes modificações, secundárias tardias com 37,1%, iniciais, 35,1%, umbrófilas, 26,6%, e as pioneiras, 1,2%. Na análise quanto a pioneiras e não pioneiras, a riqueza de espécies não-pioneiras foi 57,3%, e pioneiras, 42,6%. Quanto ao número de indivíduos, as não-pioneiras apresentaram 63,7% e as pioneiras 36,3% (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf3"><span class="sci-ico-fileFigure"></span>figuras 3 a, b</a>). Esses resultados são semelhantes quando comparamos as duas classificações sucessionais. Nesta área há maior número de pioneiras em relação à área A.</p>
+<p>Na área C, as espécies secundárias iniciais ainda predominam, com 32,1%, em seguida estão as espécies pioneiras, com 28,57%, as secundárias tardias, com 21,4% e, as umbrófilas, com 17,9%. Nas análises de abundância, as pioneiras predominam com 40%, secundárias iniciais, 29,3%, tardias, 19,7%, e umbrófilas, 11%. Nesta área ocorre o oposto das outras duas áreas, pois as pioneiras se destacam, sendo essa diferença mais expressiva nas análises por abundância. As espécies pioneiras apresentaram 60,7% do total de espécies e as não-pioneiras 39,3%. Já a abundância de pioneiras e não pioneiras foi 69,3% e 30,7% respectivamente (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf4"><span class="sci-ico-fileFigure"></span>figuras 4 a, b</a>). De modo geral, essa área se diferencia das outras não só pelo aumento das espécies que sobrevivem em condições de luz, mas também a diminuição das espécies que vivem sobre condições de sombra, mostrando assim, que se trata de uma área mais aberta, com dossel mais falho, facilitando a presença de luz direta no solo.</p>
+<p>Na área A as espécies secundárias tardias destacam-se pela dominância, densidade e riqueza, revelando que as espécies desse estágio estão fortemente presentes no dossel da floresta como também nos estratos inferiores.</p>
+<p>Na área B as espécies secundárias iniciais destacam-se pela dominância, porém, nos parâmetros densidade e riqueza, as iniciais se igualam com as tardias. Esses resultados mostram que o dossel nessa área é composto, principalmente, pelas iniciais. Nos estratos inferiores os dois grupos estão fortemente presentes.</p>
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+<strong>Figura 2</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 2</strong><br>a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na área C ocorre o oposto, pois, as espécies pioneiras destacam-se pela dominância, mostrando que nesse trecho as pioneiras estão presentes no dossel, porém nos parâmetros de densidade e riqueza, as pioneiras perdem o pódio, dando lugar para as espécies secundárias e umbrófilas.</p>
+<p>As espécies umbrófilas aumentam da área C para A, indicando que a área A está em fase mais avançada de sucessão, aumentando a predominância das espécies típicas de sub-bosque neste estrato (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf5"><span class="sci-ico-fileFigure"></span>figuras 5 a, b, c</a>).</p>
+<p>Em complemento à análise da classificação sucessional, foram elaborados perfis diagramas totais de cada uma delas, com a representação dos indivíduos amostrados seguindo a sequência da planilha de campo. Os indivíduos indicados na coloração amarela são representados pelas pioneiras; verdes claras, secundárias iniciais; verdes escuras, tardias; e as vermelhas, espécies umbrófilas.</p>
+<p>Na área A, o dossel é predominantemente composto pelas tardias, no estrato intermediário predominam as iniciais, enquanto no sub-bosque predominam espécies umbrófilas. Ocorreram três indivíduos de espécies pioneiras, desses, dois no estrato intermediário em direção ao dossel e um no sub-bosque (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf6"><span class="sci-ico-fileFigure"></span>figura 6</a>).</p>
+<p>Na área B, predominam secundárias iniciais no dossel; no estrato intermediário, além das iniciais, também ocorrem as tardias; o sub-bosque têm representantes de todos os grupos sucessionais, mas com baixa representatividade das pioneiras, com apenas cinco indivíduos (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf7"><span class="sci-ico-fileFigure"></span>figura 7</a>).</p>
+<p>Na área C, há predomínio das pioneiras no dossel, cuja altura é mais baixa que A e B. Já no estrato intermediário predominam pioneiras e secundárias iniciais e, no sub-bosque, estão presentes espécies pioneiras, secundárias iniciais e tardias, havendo poucas espécies umbrófilas (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf8"><span class="sci-ico-fileFigure"></span>figura 8</a>).</p>
+<p>De modo geral, observa-se que as três áreas são distintas, pois, na área A, as espécies estão distribuídas conforme o esperado para um final de sucessão, com o predomínio das secundárias tardias no dossel; já na área B, ocorre o predomínio das secundárias iniciais no dossel e, nos outros estratos, há todos os grupos sucessionais presentes, resultando em um grande número de indivíduos e, na área C, as pioneiras estão bem representadas em todos os estratos.</p>
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+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 3</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 3</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f4">
+<a name="f4"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf4"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 4</strong><br>a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 4</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Com base na distribuição dos grupos sucessionais, a área A está em estágio mais avançado ou final na sucessão, a área B em um estágio intermediário e, área C, em estágio mais inicial.</p>
+<p>Estratificação florestal e distribuição diamétrica - Na área A, aproximadamente 64% (204) dos indivíduos amostrados apresentam até 12 m de altura, 17% (59 ind.) entre 12,1 e 20 m, 15% entre 20,1 e 28 m e 4% entre 28,1 e 36 m (21 ind.). Essa distribuição de indivíduos apresenta formato de “J invertido” (maior número de indivíduos nas menores classes de altura, diminuindo nas maiores classes). A grande concentração de indivíduos na primeira classe de altura deve-se pela abundância das espécies umbrófilas, principalmente <i>P. suterella</i> (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf9"><span class="sci-ico-fileFigure"></span>figura 9</a>).</p>
+<p>Na área B, aproximadamente 59% (238) dos indivíduos amostrados apresentam até 12 m de altura, 25% (102 ind.) entre 12,1 e 20 m, 12% entre 20,1 e 28 m. e 4% entre 28,1 e 36 m (59 ind.). Poucos indivíduos passam dos 30 metros de altura (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf10"><span class="sci-ico-fileFigure"></span>figura 10</a>).</p>
+<p>Já na área C, aproximadamente 65% (196) dos indivíduos amostrados apresentam até 12 m de altura, 28% (83 ind.) entre 12,1 e 20 m. e 7% (21 ind.) acima dos 20 m. (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf11"><span class="sci-ico-fileFigure"></span>figura 11</a>).</p>
+<p>Ao compararmos as três áreas de estudo, quanto à distribuição das classes de altura, podemos constatar que as áreas A e B são similares quanto à porcentagem dos indivíduos em diferentes estratos. Em ambas as áreas há a predominância das secundárias tardias e iniciais nos diferentes estratos, com exceção do sub-bosque que em A possui exclusivamente espécies deste estrato (umbrófilas), enquanto em B ocorrem também indivíduos jovens de espécies secundárias. Por outro lado, na área C, a porcentagem dos indivíduos na classe até 12 m de altura é bem menor em relação às áreas A e B; as espécies pioneiras estão representadas em todos os estratos dessa floresta e, no sub-bosque há representantes de todas as categorias sucessionais.</p>
+<p>Similaridade, agrupamento e ordenação entre as áreas de estudo - Na análise utilizando o coeficiente Canberra (UPGMA), as parcelas de um mesmo bloco mantêm-se de uma forma geral em um mesmo grupo, confirmando que as áreas de estudo (A, B e C) diferem entre si. No primeiro grupo, onde se encontram as parcelas da área A, há somente uma única parcela (12) que pertence a B; porém o segundo e o terceiro grupos reconhecidos nesta análise reúnem exclusivamente parcelas das áreas B e C respectivamente (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf12"><span class="sci-ico-fileFigure"></span>figura 12</a>). O agrupamento da parcela 12 (área B) com as parcelas 1 a 10 (área A), pode ser explicada como uma parcela cuja floresta está em fase mais final de sucessão. É comum nas florestas ter parcelas em fases distintas, podendo ser causadas pela presença de uma mancha mais antiga, clareiras ou efeitos de borda. As análises de ordenação e classificação mostram esses efeitos.</p>
+<div class="row fig" id="f5">
+<a name="f5"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf5"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 5</strong><br>a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br><strong>Figure 5</strong><br>a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f6">
+<a name="f6"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf6"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 6</strong><br>Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 6</strong><br>Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f7">
+<a name="f7"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf7"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 7</strong><br>Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 7</strong><br>Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Na análise de ordenação, utilizou-se a Análise de Correspondência (CA) e a matriz de número de indivíduos por espécie. Os eixos 1, 2 e 3 correspondem a 11,8, 8,5 e 6,1 por cento da inércia total encontrada, totalizando-se 26,4%. Podemos observar que as parcelas da área C estão separadas em todos os eixos (plano horizontal e vertical), sendo esta a mais diferente em relação às demais. As áreas A e B estão separadas mais no eixo 2 (plano horizontal), ou seja, em relação ao número de indivíduos, estão mais próximas, possivelmente devido às espécies tardias já estarem presentes nos estratos inferiores da área B (<a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf13"><span class="sci-ico-fileFigure"></span>figuras 13</a> to <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalFigf14"><span class="sci-ico-fileFigure"></span>14</a>).</p>
+<p>Tanto as análises de classificação quanto as de ordenação mostram, de uma forma geral, a formação de três grupos que correspondem às três áreas de estudo, havendo maior proximidade entre as áreas A e B devido a uma maior presença das espécies tardias em ambas as áreas.</p>
+<p>Síndrome de dispersão - As espécies zoocóricas destacaram-se em todas as áreas estudadas, A, B e C (85%, 88% e 70%, respectivamente). As anemocóricas apresentaram valores mais altos na área C, em virtude do maior número de pioneiras encontradas nesta última. Já as autocóricas estão em menor número na área B.</p>
+<p>Espécies ameaçadas de extinção - Do total de 115 espécies apuradas neste estudo, conforme consta na <a href="" class="open-asset-modal" data-toggle="modal" data-target="#ModalTablet4"><span class="sci-ico-fileTable"></span>tabela 4</a>, sete espécies (6,1%) enquadram-se em uma das categorias de grau de ameaça nas três listas existentes. <i>Ocotea catharinensis,</i> presente nas três áreas de estudo, está como vulnerável (VU) nas listas de São Paulo, do Brasil e IUCN; <i>Cedrela fissilis</i>, presente somente na área B, apresentou-se como VU nas listas de São Paulo e do Brasil, e em perigo (EN) na lista da IUCN; <i>Trichilia silvatica</i>, presente nas áreas A e B, e <i>Eugenia prasina</i>, na área B, estão representadas como VU somente na lista da IUCN; <i>Virola bicuhyba</i> presente somente na área B, encontra-se EN nas listas de São Paulo e do Brasil; <i>Pouteria bullata</i>, presente somente na área B, é considerada EN na lista de São Paulo e Brasil e VU na lista da IUCN; <i>E. cantareirae</i> presente somente na área A, na lista do Brasil está como EN e na lista de São Paulo está como extinta (EX).</p>
+<div class="row fig" id="f8">
+<a name="f8"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf8"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 8</strong><br>Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 8</strong><br>Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f9">
+<a name="f9"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf9"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 9</strong><br>Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 9</strong><br>Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<h1 class="articleSectionTitle">Discussão</h1>
+<p>Composição Florística - As famílias Myrtaceae e Lauraceae também foram as mais ricas em outros estudos realizados na Floresta Ombrófila Densa Montana no Estado de São Paulo por <span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. (1993)</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Garcia &amp; Pirani (2001)</strong><span class="refCtt closed"><span>Garcia, R.J.F. &amp; Pirani, J.R. 2001. Estudo florístico dos componentes arbóreos e arbustivo da mata do Parque Santo Dias, São Paulo, SP, Brasil. Boletim de Botânica Universidade de São Paulo 19: 15-42.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Alves &amp; Metzger (2006)</strong><span class="refCtt closed"><span>Alves, L.F. &amp; Metzger, J.P. 2006. A regeneração florestal em áreas de floresta secundária na Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Ogata &amp; Gomes (2006)</strong><span class="refCtt closed"><span>Ogata, R. &amp; Gomes, E.P.C. Estrutura e composição da vegetação no Parque CEMUCAM, Cotia, SP. Hoehnea 33(3): 371-384.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, trabalhos realizados no município de São Paulo e arredores, e no interior do Estado, por <span class="ref"><strong class="xref xrefblue">Ivanauskas (1997)</strong><span class="refCtt closed"><span>Ivanauskas, N. M. 1997. Caracterização florística e fisionômica da Floresta Atlântica sobre a formação Pariquera-Açu, na Zona da Morraria Costeira do Estado de São Paulo. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Sztutman &amp; Rodrigues (2002)</strong><span class="refCtt closed"><span>Sztutman, M. &amp; Rodrigues, R.R. 2002. O mosaico vegetacional numa área de floresta contínua da planície litorânea, Parque Estadual da Campina do Encantado, Pariquera-Açu, SP. Revista Brasileira de Botânica 25(2): 161-176.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>, sendo que neste último estudo somente Myrtaceae destacou-se pela sua riqueza.</p>
+<p>Os gêneros <i>Cinnamomum, Eugenia, Mollinedia, Myrcia</i> e <i>Ocotea</i> também se destacaram em outros levantamentos realizados no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>), <i>Nectandra</i> também se destacou no levantamento realizado no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <i>Eugenia, Myrcia</i> e <i>Ocotea</i>, por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span> em remanescentes de Floresta Ombrófila Densa Montana situados na região metropolitana de São Paulo, <i>Eugenia</i> e <i>Ocotea,</i> por <span class="ref"><strong class="xref xrefblue">Aguiar <i>et al</i>. (2001)</strong><span class="refCtt closed"><span>Aguiar, O.T., Pastore, J.A., Rocha, F.T., Baitello, J.B. 2001. Flora fanerogâmica de um trecho da Floresta Densa Secundária do Parque Estadual da Serra do Mar - Núcleo Cunha Indaiá - SP. Disponível em https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf (acesso em 18-V-2020).</span><br><a href="https://smastr16.blob.core.windows.net/iflorestal/ifref/RIF13-1/RIF13-1_1-18.pdf" target="_blank">https://smastr16.blob.core.windows.net/i...
+            </a></span></span> na região de Cunha e somente <i>Eugenia</i> por <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> no município de Miracatu.</p>
+<div class="row fig" id="f10">
+<a name="f10"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf10"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 10</strong><br>Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 10</strong><br>Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f11">
+<a name="f11"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf11"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 11</strong><br>Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 11</strong><br>Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p>Parâmetros fitossociológicos - Os valores totais, desde estudo, de densidade absoluta de 1700 ind. ha<sup>-1</sup> e dominância absoluta de 39,8 m<sup>2</sup> ha<sup>-1</sup> são compatíveis com os encontrados em outros trechos do PEC (<span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. 1993</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>), onde a densidade absoluta variou entre 1248 a 2295 ind./ha e a dominância entre 35,7 a 48,4 m<sup>2</sup> ha<sup>-1</sup>. Em estudo realizado em São Paulo e nos municípios vizinhos de Cotia e Itapevi (<span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>) os valores de densidade variaram entre 1425 a 1760 ind. ha<sup>-1</sup> e de dominância entre 44,5 a 49,3 m<sup>2</sup> ha<sup>-1</sup>, também compatíveis com os do presente estudo.</p>
+<p>Em outros trechos da floresta do PEC estudados por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, também foram encontradas <i>H. silvianii</i> e <i>A. olivaceum</i> entre as espécies mais dominantes, e em Itapevi, somente <i>H. silvianii</i> (<span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>). <span class="ref"><strong class="xref xrefblue">Klein (1990)</strong><span class="refCtt closed"><span>Klein, R.M. 1990. Estrutura, composição florística, dinamismo e manejo da Mata Atlântica (Floresta Ombrófila Densa) do Sul do Brasil. In: Simpósio de Ecossistemas da Costa Sul e Sudeste Brasileira: Estrutura, funções e manejo, 2 Águas de Lindóia, 1990. Anais... Academia de Ciências do Estado de São Paulo. pp. 259-286.</span></span></span> destaca <i>A. olivaceum</i> como uma das espécies mais importantes nas encostas das Serras do Sul do país e cita que <i>E. cantareirae</i> está associada a florestas em sucessão avançada. Sendo que esta também se destacou no estudo realizado no PEC por <span class="ref"><strong class="xref xrefblue">Baitello <i>et al</i>. (1993)</strong><span class="refCtt closed"><span>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</span></span></span>. Ainda, <span class="ref"><strong class="xref xrefblue">Blum &amp; Roderjan (2007)</strong><span class="refCtt closed"><span>Blum, C.T. &amp; Roderjan, C.V. 2007. Espécies indicadoras em um gradiente da Floresta Ombrófila na Serra da Prata, Paraná, Brasil. Revista Brasileira de Biociências 5(2): 873-875.</span></span></span> citam a <i>E. cantareirae</i> como espécie indicadora de formação de Floresta Ombrófila Densa Montana.</p>
+<p>A espécie <i>P. suterella</i> também se destacou em outros fragmentos do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e na Floresta Ombrófila Densa Montana das encostas de Paranapiacaba (<span class="ref"><strong class="xref xrefblue">Lima <i>et al</i>. 2011</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>), sendo que <span class="ref"><strong class="xref xrefblue">Bertani (2006)</strong><span class="refCtt closed"><span>Bertani, D. F. 2006. Ecologia de populações de Psychotria suterella Müll. Arg. (Rubiaceae) em uma paisagem fragmentada de Mata Atlântica. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> relata que essa espécie frequentemente se destaca pelo seu valor de densidade nos fragmentos florestais do Estado de São Paulo.</p>
+<p><i>A. triplinervia, H. silvianii, C. canjerana, C. obliqua</i> e <i>P. floribundum</i> destacaram-se por seus valores de dominância em outros trechos do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>). Em alguns levantamentos realizados no Estado de São Paulo, <i>A. triplinervia</i> destacou-se pelo seu valor de importância (<span class="ref"><strong class="xref xrefblue">Ivanauskas 1997</strong><span class="refCtt closed"><span>Ivanauskas, N. M. 1997. Caracterização florística e fisionômica da Floresta Atlântica sobre a formação Pariquera-Açu, na Zona da Morraria Costeira do Estado de São Paulo. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Arzolla 2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Barretto 2013</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>). Esta espécie ocorre somente na forma de indivíduos mais velhos nas florestas mais maduras, geralmente esparsos, sendo, por isso, rara, pois não se vê na regeneração (<span class="ref"><strong class="xref xrefblue">Klein 1984</strong><span class="refCtt closed"><span>Klein, R.M. 1984. Aspectos Dinâmicos da Vegetação do Sul do Brasil. Sellowia 36: 5-54.</span></span></span>, <span class="ref"><sup class="xref xrefblue">1990</sup><span class="refCtt closed"><span>Klein, R.M. 1990. Estrutura, composição florística, dinamismo e manejo da Mata Atlântica (Floresta Ombrófila Densa) do Sul do Brasil. In: Simpósio de Ecossistemas da Costa Sul e Sudeste Brasileira: Estrutura, funções e manejo, 2 Águas de Lindóia, 1990. Anais... Academia de Ciências do Estado de São Paulo. pp. 259-286.</span></span></span>). Na área de estudo, não foram observados indivíduos jovens desta espécie. No levantamento realizado por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al</i>. (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, dentre essas espécies, somente <i>C. obliqua</i> se assemelha com este estudo.</p>
+<div class="row fig" id="f12">
+<a name="f12"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf12"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 12</strong><br>Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.<br><strong>Figure 12</strong><br>Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.<br>
+</div>
+</div>
+<div class="row fig" id="f13">
+<a name="f13"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf13"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 13</strong><br>Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 13</strong><br>Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<div class="row fig" id="f14">
+<a name="f14"></a><div class="col-md-4 col-sm-4"><a href="" data-toggle="modal" data-target="#ModalFigf14"><div class="thumbOff">
+<img src=""><div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8 col-sm-8">
+<strong>Figura 14</strong><br>Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Figure 14</strong><br>Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</div>
+</div>
+<p><i>C. oblongifolia</i> destacou-se nos levantamentos de <span class="ref"><strong class="xref xrefblue">Arzolla (2002</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <span class="ref"><sup class="xref xrefblue">2011</sup><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>. Em outro trecho estudado por <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>, <i>C. floribundus</i> e <i>A. triplinervia</i> também se destacaram. <i>Piptocarpha macropoda</i> também foi encontrada em alta frequência em trecho do PEC (<span class="ref"><strong class="xref xrefblue">Arzolla 2011</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span>) e no levantamento feito por <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> na Floresta Ombrófila Densa do Vale do Ribeira</p>
+<p>Análises grupos ecológicos - No estudo realizado por <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, em seu levantamento geral de espécies tardias, a percentagem apresentou o dobro do que encontrado neste estudo. Mas essa diferença pode ser pelo fato de que o autor considerou as espécies umbrófilas como parte das secundárias tardias.</p>
+<p>Em outro estudo realizado no PEC por <span class="ref"><strong class="xref xrefblue">Arzolla (2002)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</span></span></span>, as tardias destacaram-se três vezes a mais que as iniciais, mas lembrando que o autor considerou também naquele trabalho, assim como Barretto, as umbrófilas como parte das espécies tardias.</p>
+<p>O trabalho realizado por <span class="ref"><strong class="xref xrefblue">Gandolfi <i>et al</i>. (1995)</strong><span class="refCtt closed"><span>Gandolfi, F., Leitão-Filho, H.F., Bezerra, C.L.F. 1995. Levantamento florístico e caráter sucessional das espécies arbustivo-arbóreas de uma floresta mesófila semidecidua no município de Guarulhos, SP. Revista Brasileira Biologia 55(4): 753-767.</span></span></span>, apresentou 30% de espécies pioneiras, sugerindo que o trecho estudado pelo autor se encontrava numa condição inicial em termos sucessionais. Nos estudos de <span class="ref"><strong class="xref xrefblue">Arzolla (2011)</strong><span class="refCtt closed"><span>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</span></span></span> e <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span>, as pioneiras também obtiveram percentagem expressivas (61% e 26%, respectivamente), mas os trechos referem-se a áreas de regeneração.</p>
+<p><span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, em suas análises, constatou nas três áreas estudadas por ele, em fase avançada de sucessão, alta dominância e riqueza das espécies secundárias tardias, assim como observado na área A deste estudo.</p>
+<p>Síndrome de dispersão - Em outros levantamentos realizados na Floresta Ombrófila Densa por <span class="ref"><strong class="xref xrefblue">Catharino <i>et al.</i> (2006)</strong><span class="refCtt closed"><span>Catharino, E.L., Bernacci, L.C., Franco, G.A.D.C., Durigan, G., Metzger, J.P. 2006. Aspectos da composição e diversidade do componente arbóreo das florestas da Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/ (acesso em 18-V-2020).</span><br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00306022006/" target="_blank">http://biotaneotropica.org.br/v6n2/pt/ab...
+            </a></span></span>, <span class="ref"><strong class="xref xrefblue">Lima <i>et al.</i> (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Barretto (2013)</strong><span class="refCtt closed"><span>Barretto, E.H.P. 2013. Florestas climácicas da região metropolitana de São Paulo - SP: caracterização florística, estrutural e relações fitogeográficas. São Paulo: Dissertação de Mestrado, Instituto de Botânica, São Paulo.</span></span></span>, <span class="ref"><strong class="xref xrefblue">Moura &amp; Mantovani (2017)</strong><span class="refCtt closed"><span>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</span></span></span> foram encontrados resultados semelhantes quanto à porcentagem de espécies zoocóricas. <span class="ref"><strong class="xref xrefblue">Lima <i>et al.</i> (2011)</strong><span class="refCtt closed"><span>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</span></span></span> relata que nas áreas que desenvolveu seu estudo predominam espécies zoocóricas, sendo áreas maduras da Floresta Ombrófila Densa Montana das encostas da Serra do Mar em Santo André, e <span class="ref"><strong class="xref xrefblue">Mantovani (1998)</strong><span class="refCtt closed"><span>Mantovani, W. 1998. Dinâmica da Floresta Pluvial Atlântica. Anais do IV Simpósio de Ecossistemas Brasileiros. Praia, Represa e Mata - Águas de Lindóia. ACIESP 104 v. II.</span></span></span> relata que é comum a predominância de espécies zoocóricas nessas florestas.</p>
+<p>Espécies ameaçadas de extinção - A espécie <i>E. cantareirae</i> foi classificada como vulnerável (VU) no estudo realizado por <span class="ref"><strong class="xref xrefblue">Souza <i>et al</i>. (2016)</strong><span class="refCtt closed"><span>Souza, S.C.P.M., Silva, A.G., Franco, G.A.D.C., Ivanauskas, N.M. 2016. A vegetação secundária em um fragmento florestal urbano: Influência de exóticas invasoras na comunidade vegetal. Revista do Instituto Florestal 28(1): 7-35.</span></span></span>, o que diverge com a lista atualizada de flora ameaçada do Estado de São Paulo, publicada no Diário Oficial de São Paulo - Poder Executivo - Seção I - de 07 de junho de 2016, na qual consta como extinta (EX). Essa espécie é considerada rara, no entanto tal classificação para São Paulo necessita ser revista. A presença dessas espécies mostra a importância de se conservar e cuidar desse remanescente florestal.</p>
+<h1 class="articleSectionTitle">Conclusões</h1>
+<p>Dentre as conclusões deste estudo, podemos constatar que as três áreas analisadas são floristicamente e estruturalmente diferentes, pois algumas das espécies amostradas estão presentes em todas as áreas e outras são exclusivas em apenas uma ou duas delas e mesmo quando presentes nas três áreas, não apresentam o mesmo VI em cada uma delas.</p>
+<p>Todos os grupos sucessionais (pioneiras, secundárias iniciais e tardias e umbrófilas) estão presentes nas três áreas, porém em proporções distintas e também predominando variadamente em cada um de seus estratos.</p>
+<p>Na área A, em seu dossel, há predominância de espécies secundárias tardias; estrato médio com secundárias iniciais e o sub-bosque, majoritariamente, formado por espécies umbrófilas. Esta área ainda contem baixa representatividade de espécies pioneiras e secundárias iniciais que ocorrem em pequenas clareiras e bordas da mancha estudada.</p>
+<p>Na área B, as espécies secundárias iniciais predominam tanto no dossel quanto no estrato médio da floresta e o sub-bosque é formado por todos os grupos sucessionais, exceto as pioneiras, estas com baixa representatividade e, quando presentes, estão restritas a pequenas clareiras, o mesmo que ocorre na área A.</p>
+<div class="row table" id="t4">
+<a name="t4"></a><div class="col-md-4 col-sm-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
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+<div class="col-md-8 col-sm-8">
+<strong><strong>Tabela 4</strong></strong><br> Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.<br><strong><strong>Table 4</strong></strong><br> List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.<br>
+</div>
+</div>
+<p>A área C possui dossel descontínuo com predomínio de pioneiras; o estrato médio apresenta predomínio de pioneiras e iniciais, mas com poucas tardias e umbrófilas. As clareiras dessa área são maiores que em A e B. As espécies pioneiras compõem o dossel desta floresta.</p>
+<p>Conclui-se, pela análise, que a área A está em processo de sucessão mais avançado ou final, a área B em fase intermediária e, a C, em uma fase mais inicial das anteriores.</p>
+<p>Avaliar o estágio successional de uma determinada área é um grande desafio científico, com importantes implicações na conservação. Conhecer a floresta em diferentes estágios traz subsídios a medidas aplicadas visando a recuperação, não somente do Parque Estadual da Cantareira, como da Serra da Cantareira e demais áreas da Floresta Ombrófila Densa Montana. A floresta do Parque Estadual da Cantareira, especificamente no Núcleo Pedra Grande, apesar de haver sofrido grande pressão antrópica, ainda abriga remanescentes florestais preservados, dos quais a área A é um exemplo, que servem como fonte de sementes e outras unidades de dispersão para a recuperação natural dos trechos em estágio sucessional em fases intermediária a inicial, como as áreas B e C do presente estudo.</p>
+<p>Estudos de recuperação natural da vegetação nativa em florestas do Planalto Paulista além de serem escassos, são de grande importância para garantir às gerações futuras a manutenção dos serviços ecossistêmicos da Floresta Ombrófila Densa, a Mata Atlântica, hoje ainda bastante afetada pela fragmentação e consequente perda de biodiversidade.</p>
+</div>
+<div class="articleSection" data-anchor="Agradecimentos">
+<h1 class="articleSectionTitle">Agradecimentos</h1>
+<p>Agradecemos ao Conselho Nacional de Desenvolvimento Científico e Tecnológico, pela Bolsa de Mestrado concedida à primeira Autora (Processo nº 133843/2018-9) junto ao Programa de Pós-Graduação em Biodiversidade Vegetal e Meio Ambiente do Instituto de Botânica de São Paulo.</p>
+</div>
+<div class="articleSection" data-anchor="Literatura Citada">
+<h1 class="articleSectionTitle">Literatura Citada</h1>
+<div class="ref-list"><ul class="refList">
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+</div></li>
+<li><div>Alves, L.F. &amp; Metzger, J.P. 2006. A regeneração florestal em áreas de floresta secundária na Reserva Florestal do Morro Grande, Cotia, SP. Biota Neotropica 6(2). Disponível em http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/ (acesso em 18-V-2020).<br><a href="http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/" target="_blank">» http://biotaneotropica.org.br/v6n2/pt/abstract?article+bn00406022006/</a>
+</div></li>
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+<li><div>Aragaki, S. 1997. Florística e estrutura de trecho remanescente de floresta no Planalto Paulistano (SP). São Paulo: Dissertação de Mestrado, Universidade de São Paulo, São Paulo.</div></li>
+<li><div>Arzolla, F.A.R.D.P. 2002. Florística e Fitossociologia de Trecho da Serra da Cantareira, Núcleo Águas Claras, Parque Estadual da Cantareira, Mairiporã - SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</div></li>
+<li><div>Arzolla, F.A.R.D.P. 2011. Florestas secundárias e a regeneração natural de clareiras antrópicas na Serra da Cantareira, SP. Tese de Doutorado, Universidade Estadual de Campinas, Campinas.</div></li>
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+<li><div>Baitello, J.B., Aguiar, O.T., Rocha, F.T., Pastore, J.A., Esteves, R. 1993. Estrutura Fitossociológica da Vegetação Arbórea da Serra da Cantareira (SP) - Núcleo Pinheirinho. Revista do Instituto Florestal 5 (2): 133-161.</div></li>
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+</div></li>
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+<li><div>Flora do Brasil 2020 em construção. Jardim Botânico do Rio de Janeiro. Disponível em (http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964) (acesso em 11-III-2020).<br><a href="http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964" target="_blank">» http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB10964</a>
+</div></li>
+<li><div>Fundação SOS Mata Atlântica - Aqui tem Mata. Disponível em (http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo) (acesso em 26-I-2020).<br><a href="http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo" target="_blank">» http://aquitemmata.org.br/#/busca/sp/S%C3%A3o%20Paulo/S%C3%A3o%20Paulo</a>
+</div></li>
+<li><div>Gandolfi, F. 1991. Estudo florístico e fitossociológico de uma floresta residual na área do Aeroporto Internacional de São Paulo, Município de Guarulhos, SP. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</div></li>
+<li><div>Gandolfi, F., Leitão-Filho, H.F., Bezerra, C.L.F. 1995. Levantamento florístico e caráter sucessional das espécies arbustivo-arbóreas de uma floresta mesófila semidecidua no município de Guarulhos, SP. Revista Brasileira Biologia 55(4): 753-767.</div></li>
+<li><div>Garcia, R.J.F. &amp; Pirani, J.R. 2001. Estudo florístico dos componentes arbóreos e arbustivo da mata do Parque Santo Dias, São Paulo, SP, Brasil. Boletim de Botânica Universidade de São Paulo 19: 15-42.</div></li>
+<li><div>Gómez-Pompa, A. 1971. Posible papel de la vegetación secundaria en la evolución de la flora tropical. Biotropica 3: 125-135.</div></li>
+<li><div>IBGE. 2012. Fundação Instituto Brasileiro de geografia e Estatística. Manual técnico da vegetação brasileira. 2<sup>ed</sup>, Rio de Janeiro.</div></li>
+<li><div>IBGE. Fundação Instituto Brasileiro de Geografia e Estatística. Disponível em http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html (acesso em 16-XI-2019).<br><a href="http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html" target="_blank">» http://7a12.ibge.gov.br/vamos-conhecer-o-brasil/nosso-territorio/biomas.html</a>
+</div></li>
+<li><div>Ivanauskas, N. M. 1997. Caracterização florística e fisionômica da Floresta Atlântica sobre a formação Pariquera-Açu, na Zona da Morraria Costeira do Estado de São Paulo. Dissertação de Mestrado, Universidade Estadual de Campinas, Campinas.</div></li>
+<li><div>Kageyama, P.Y. &amp; Castro, C.F.A. 1989. Sucessão secundária, Estrutura genética e Plantações de espécies arbóreas nativas. Instituto de Pesquisas e Estudos Florestais 41/42: 83-93.</div></li>
+<li><div>Klein, R.M. 1984. Aspectos Dinâmicos da Vegetação do Sul do Brasil. Sellowia 36: 5-54.</div></li>
+<li><div>Klein, R.M. 1990. Estrutura, composição florística, dinamismo e manejo da Mata Atlântica (Floresta Ombrófila Densa) do Sul do Brasil. In: Simpósio de Ecossistemas da Costa Sul e Sudeste Brasileira: Estrutura, funções e manejo, 2 Águas de Lindóia, 1990. Anais... Academia de Ciências do Estado de São Paulo. pp. 259-286.</div></li>
+<li><div>Köppen, G. Classificação Climática de Koppen-Geiser. Disponível em https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf (acesso em 17-XI-2019).<br><a href="https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf" target="_blank">» https://portais.ufg.br/up/68/o/Classifica____o_Clim__tica_Koppen.pdf</a>
+</div></li>
+<li><div>Leitão-Filho, H.F. 1987. Considerações sobre a florística de florestas tropicais e sub-tropicais do Brasil. IPEF 45: 41-46.</div></li>
+<li><div>Leite, M. 2007. Nos caminhos da Biodiversidade Paulista / Nas Costas do Brasil. Os litorais paulistas. São Paulo: Secretaria do Meio Ambiente: Instituto Amigos da Reserva da Biosfera da Mata Atlântica: Imprensa oficial do Estado de São Paulo.</div></li>
+<li><div>Lima, M.E.L., Cordeiro, I., Moreno, P.R.H. 2011. Estrutura do componente arbóreo em Floresta Ombrófila Densa Montana no Parque Natural Municipal Nascentes de Paranapiacaba (PNMNP), Santo André, SP, Brasil. Hoehnea 38(1): 73-96.</div></li>
+<li><div>Lino, C.F. &amp; Amaral, M.M. 2018. Mata Atlântica e Sociobiodiversidade: Desafios e caminhos para a sustentabilidade. CN-RBMA Conselho Nacional da Reserva da Biosfera da Mata Atlântica. São Paulo: IA- RBMA.</div></li>
+<li><div>Mantovani, W. 1998. Dinâmica da Floresta Pluvial Atlântica. Anais do IV Simpósio de Ecossistemas Brasileiros. Praia, Represa e Mata - Águas de Lindóia. ACIESP 104 v. II.</div></li>
+<li><div>Moura, C. &amp; Mantovani, W. 2017. Regeneração natural da Floresta Ombrófila Densa após oito anos de abandono de atividades agrícolas em Miracatú, Vale do Ribeira, SP. Revista do Instituto Florestal 29(1): 91-119.</div></li>
+<li><div>Mueller-Dombois, D. &amp; Ellenberg, H. 1974. Aims and methods of vegetation ecology. New York: John Wiley &amp; Sons.</div></li>
+<li><div>Myers, N., Mittermeier, R.A., Mittermeier, C.G., Fonseca, G.A.B. 2000. Kent, J. Biodiversity hotspots for conservation priorities. Nature 403: 853-845.</div></li>
+<li><div>Ogata, R. &amp; Gomes, E.P.C. Estrutura e composição da vegetação no Parque CEMUCAM, Cotia, SP. Hoehnea 33(3): 371-384.</div></li>
+<li><div>Polisel, R.T. &amp; Franco, G.A.D.C. 2007. Caracterização sucessional de uma floresta secundária com 40 anos de idade em Juquitiba, SP. Revista Brasileira de Biociências 5(supl. 2): 387-389.</div></li>
+<li><div>Rocha, A.A. &amp; Costa, J.P.O. 1998. A Reserva da Biosfera da Mata Atlântica e sua aplicação no Estado de São Paulo: apresentação Covas, M.; prefácio Feldmann, F. J. - São Paulo: Terra Virgem, Secretaria do Meio Ambiente do Estado de São Paulo.</div></li>
+<li><div>Rodrigues, R.R. &amp; Shepherd, G.J. 1992. Análise da variação estrutural e fisionômica da vegetação e características edáficas, num gradiente altitudinal na Serra do Japi. <i>In</i>: L.P.C. Morellato (org.). História natural da Serra do Japi: ecologia e preservação de uma área florestal no sudeste do Brasil. Editora Unicamp: Campinas, pp. 64-96.</div></li>
+<li><div>São Paulo. 2010. Secretaria do Meio Ambiente. Plano de Manejo do Parque Estadual da Cantareira. São Paulo: Fundação Florestal.</div></li>
+<li><div>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</div></li>
+<li><div>Shepherd, G. J. 2010. Fitopac 2.1. Manual do usuário. Campinas: UNICAMP.</div></li>
+<li><div>Souza, S.C.P.M., Silva, A.G., Franco, G.A.D.C., Ivanauskas, N.M. 2016. A vegetação secundária em um fragmento florestal urbano: Influência de exóticas invasoras na comunidade vegetal. Revista do Instituto Florestal 28(1): 7-35.</div></li>
+<li><div>Swaine, M.D. &amp; Whitmore, T.C. 1988. On the definition of ecological species groups in tropical rain forests. Vegetation 75: 81-86.</div></li>
+<li><div>Sztutman, M. &amp; Rodrigues, R.R. 2002. O mosaico vegetacional numa área de floresta contínua da planície litorânea, Parque Estadual da Campina do Encantado, Pariquera-Açu, SP. Revista Brasileira de Botânica 25(2): 161-176.</div></li>
+<li><div>Tabarelli, M. 1994. Clareiras naturais e a dinâmica sucessional de um trecho de floresta na Serra da Cantareira, SP. Dissertação Mestrado, Universidade de São Paulo, São Paulo.</div></li>
+<li><div>Whitmore, T.C. 1989. Canopy gaps and the major groups of florest trees. Ecology 70(3): 536-538.</div></li>
+</ul></div>
+</div>
+<div class="articleSection" data-anchor="Datas de Publicação ">
+<h1 class="articleSectionTitle">Datas de Publicação </h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Publicação nesta coleção</strong><br>24 Jan 2022</li>
+<li>
+<strong>Data do Fascículo</strong><br>2022</li>
+</ul></div></div>
+</div>
+<div class="articleSection" data-anchor="Histórico">
+<h1 class="articleSectionTitle">Histórico</h1>
+<div class="row"><div class="col-md-12 col-sm-12"><ul class="articleTimeline">
+<li>
+<strong>Recebido</strong><br>13 Out 2020</li>
+<li>
+<strong>Aceito</strong><br>03 Nov 2021</li>
+</ul></div></div>
+</div>
+<section class="documentLicense"><div class="container-license"><div class="row">
+<div class="col-sm-3 col-md-2"><a href="http://creativecommons.org/licenses/by/4.0/" target="_blank" title=""><img src="https://licensebuttons.net/l/by/4.0//88x31.png" alt="Creative Common - by 4.0 "></a></div>
+<div class="col-sm-9 col-md-10"><a href="http://creativecommons.org/licenses/by/4.0/" target="_blank" title="">Este é um artigo publicado em acesso aberto (Open Access) sob a licença Creative Commons Attribution, que permite uso, distribuição e reprodução em qualquer meio, sem restrições desde que o trabalho original seja corretamente citado.</a></div>
+</div></div></section></article>
+</div>
+</div></div></section><div class="modal fade ModalDefault ModalTutors" id="ModalTutors" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
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+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Sobre os autores</h4>
+</div>
+<div class="modal-body">
+<div class="info">
+<div class="tutors">
+<strong> Rafaela Dias Valeck da Silva </strong><strong>4</strong><br><div>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-9049-3704" class="btnContribLinks orcid">http://orcid.org/0000-0002-9049-3704</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Inês Cordeiro </strong><br><div>Instituto de Botânica, Avenida Miguel Estefano, 3.687, 04301-902 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0002-2626-5280" class="btnContribLinks orcid">http://orcid.org/0000-0002-2626-5280</a></li></ul>
+<div class="clearfix"></div>
+</div>
+<div class="tutors">
+<strong> Frederico Alexandre Roccia Dal Pozzo Arzolla </strong><br><div>Instituto Florestal, Rua do Horto, 931, 02377-000 São Paulo, SP, Brasil</div>
+<ul class="md-list inline"><li><a href="http://orcid.org/0000-0003-3111-6877" class="btnContribLinks orcid">http://orcid.org/0000-0003-3111-6877</a></li></ul>
+<div class="clearfix"></div>
+</div>
+</div>
+<div class="info"><div>Editora Associada: Cláudia Baider</div></div>
+<div class="info">1<div>Parte da Dissertação de Mestrado do primeiro Autor</div>
+</div>
+<div class="info">4 Autora para correspondência: <a href="mailto:rafaela_valeck@hotmail.com">rafaela_valeck@hotmail.com</a>
+</div>
+</div>
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+<div class="modal fade ModalDefault" id="ModalTablesFigures" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">Figuras | Tabelas</h4>
+</div>
+<div class="modal-body">
+<ul class="nav nav-tabs md-tabs" role="tablist">
+<li role="presentation" class="col-md-4 col-sm-4 active"><a href="#figures" aria-controls="figures" role="tab" data-toggle="tab">Figuras
+                    (14)
+                </a></li>
+<li role="presentation" class="col-md-4 col-sm-4 "><a href="#tables" aria-controls="tables" role="tab" data-toggle="tab">Tabelas
+                    (4)
+                </a></li>
+</ul>
+<div class="clearfix"></div>
+<div class="tab-content">
+<div role="tabpanel" class="tab-pane active" id="figures">
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 1</strong><br>Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.</div>
+<div class="col-md-8">
+<strong>Figure 1</strong><br>Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 2</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 2</strong><br>a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 3</strong><br>a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 3</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 4</strong><br>a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 4</strong><br>a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf5"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 5</strong><br>a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 5</strong><br>a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf6"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 6</strong><br>Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 6</strong><br>Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf7"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 7</strong><br>Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 7</strong><br>Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf8"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 8</strong><br>Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 8</strong><br>Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf9"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 9</strong><br>Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 9</strong><br>Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf10"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 10</strong><br>Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 10</strong><br>Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf11"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 11</strong><br>Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 11</strong><br>Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf12"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 12</strong><br>Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.</div>
+<div class="col-md-8">
+<strong>Figure 12</strong><br>Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf13"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 13</strong><br>Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 13</strong><br>Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row fig">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalFigf14"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong>Figura 14</strong><br>Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong>Figure 14</strong><br>Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+</div>
+<div role="tabpanel" class="tab-pane " id="tables">
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet1"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 1</strong></strong><br> Classificação Sucessional adotada por alguns autores ao longo dos anos.</div>
+<div class="col-md-8">
+<strong><strong>Table 1</strong></strong><br> Sucessional classification adopted by some authors over the years.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet2"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 2</strong></strong><br> Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.</div>
+<div class="col-md-8">
+<strong><strong>Table 2</strong></strong><br> Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet3"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 3</strong></strong><br> Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.</div>
+<div class="col-md-8">
+<strong><strong>Table 3</strong></strong><br> Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.</div>
+</div>
+<div class="row table">
+<div class="col-md-4"><a data-toggle="modal" data-target="#ModalTablet4"><div class="thumbOff">
+                        Thumbnail
+                        <div class="zoom"><span class="sci-ico-zoom"></span></div>
+</div></a></div>
+<div class="col-md-8">
+<strong><strong>Tabela 4</strong></strong><br> Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.</div>
+<div class="col-md-8">
+<strong><strong>Table 4</strong></strong><br> List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.</div>
+</div>
+</div>
+</div>
+</div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf01.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 1   Mapa com a localização das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil. Elaborado por Marina Kanashiro, 2019.<br>Figure 1   Map with the location of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Prepared by Marina Kanashiro, 2019.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf01.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf01.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf02.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 2   a. Riqueza e abundância das espécies pioneiras, secundárias iniciais, secundárias tardias e ombrófilas na área A. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área A. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 2   a. Wealth and abundance of pioneer, early secondary, late secondary and umbrophilous species in area A. b. Wealth and abundance of pioneer or non-pioneer species in area A. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf02.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf02.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf03.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 3   a. Riqueza e abundância das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área B. b. Riqueza e abundância das espécies pioneiras ou não-pioneiras na área B. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 3   a. Wealth and abundance of pioneers, early and late secondary and umbrophilous species in area B. b. Wealth and abundance of pioneer or non-pioneer species in area B. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf03.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf03.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf04.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 4   a. Riqueza e abundância sucessional das espécies pioneiras, secundárias iniciais e tardias e ombrófilas na área C. b. Riqueza e abundância das espécies - pioneiras ou não-pioneiras na área C. Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 4   a. Wealth and abundance of pioneers, early and late secondary and umbrophilous in area C. b. Wealth and abundance of pioneer or non-pioneer species in area C. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf04.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf04.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf5" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf05.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 5   a. Dominância relativa (DoR) das espécies. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. b. Densidade relativa (DeR) das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. c. Riqueza das espécies amostradas. Coloração amarela: pioneira, verde clara: secundária inicial, verde escura: secundária tardia, vermelha: umbrófila. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>Figure 5   a. Relative dominance (DoR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. b. Relative density (DeR) of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. c. Wealth of the species sampled. Yellow coloration: pioneer, light green: early secondary, dark green: late secondary, red: umbrophilous. Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf05.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf05.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf6" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf06.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 6   Diagrama de perfil da Área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 6   Profile diagram of Area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf06.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf06.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf7" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf07.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 7   Diagrama de perfil da Área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 7   Profile diagram of Area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf07.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf07.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf8" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf08.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 8   Diagrama de perfil da Área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 8   Profile diagram of Area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf08.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf08.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf9" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf09.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 9   Distribuição dos indivíduos em classes de altura na área A, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 9   Distribution of individuals in height classes in area A, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf09.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf09.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf10" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf10.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 10   Distribuição dos indivíduos em classes de altura na área B, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 10   Distribution of individuals in height classes in area B, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf10.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf10.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf11" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf11.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 11   Distribuição dos indivíduos em classes de altura na área C, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 11   Distribution of individuals in height classes in area C, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf11.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf11.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf12" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf12.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 12   Análise de classificação das parcelas das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil., pelo método UPGMA e coeficiente Canberra. Coeficiente de correlação igual a 0,7821.<br>Figure 12   Classification analysis of plots in the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil., using the UPGMA method and the Canberra coefficient. Correlation coefficient equal to 0,7821.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf12.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf12.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf13" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf13.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 13   Eixos 1 e 2 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 13   Axes 1 and 2 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf13.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf13.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalFigs" id="ModalFigf14" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><a class="link-newWindow showTooltip" target="_blank" data-placement="left" title="Abrir em nova janela" href="2236-8906-hoehnea-49-e1082020-gf14.jpg"><span class="sci-ico-newWindow"></span></a><h4 class="modal-title">
+<span class="sci-ico-fileFigure"></span>Figura 14   Eixos 1 e 3 da análise de ordenação pelo método CA das três áreas de estudo, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br>Figure 14   Axes 1 and 3 of the ordering analyses by the CA method of the three study areas, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><a href="2236-8906-hoehnea-49-e1082020-gf14.jpg"><img style="max-width:100%" src="2236-8906-hoehnea-49-e1082020-gf14.jpg"></a></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet1" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 1</strong>    Classificação Sucessional adotada por alguns autores ao longo dos anos.<br><strong>Table 1</strong>    Sucessional classification adopted by some authors over the years.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th valign="top" align="left">Ano</th>
+<th valign="top" align="center">Autor</th>
+<th valign="top" align="center">Classificação</th>
+</tr></thead>
+<tbody>
+<tr>
+<td valign="top" align="left">1965</td>
+<td valign="top" align="center">Budowski</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">1971</td>
+<td valign="top" align="center">Gómez-Pompa</td>
+<td valign="top" align="center">Primária e secundária</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1980</sup><span class="refCtt closed"><span>Denslow, J.S. 1980. Gap partitioning among tropical rainforest trees. Biotropica 12: 47-51.</span></span></span></td>
+<td valign="top" align="center">Denslow</td>
+<td valign="top" align="center">Pioneira, secundária e sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left">1989</td>
+<td valign="top" align="center">Whitmore</td>
+<td valign="top" align="center">Pioneira e Clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">1989</td>
+<td valign="top" align="center">Kageyama &amp; Castro</td>
+<td valign="top" align="center">Pioneira, clímax e sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left">1991</td>
+<td valign="top" align="center">Gandolfi</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">1992</td>
+<td valign="top" align="center">Rodrigues &amp; Shepherd</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e típica de sub-bosque</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1994</sup><span class="refCtt closed"><span>Tabarelli, M. 1994. Clareiras naturais e a dinâmica sucessional de um trecho de floresta na Serra da Cantareira, SP. Dissertação Mestrado, Universidade de São Paulo, São Paulo.</span></span></span></td>
+<td valign="top" align="center">Tabarelli</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1996</sup><span class="refCtt closed"><span>Bernacci, L.C. &amp; Leitão Filho, H.F. 1996. Flora fanerogâmica da floresta da Fazenda São Vicente, Campinas, SP. Revista Brasileira de Botânica, 19: 149-164.</span></span></span></td>
+<td valign="top" align="center">Bernacci &amp; Leitão-Filho</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">1997</sup><span class="refCtt closed"><span>Aragaki, S. 1997. Florística e estrutura de trecho remanescente de floresta no Planalto Paulistano (SP). São Paulo: Dissertação de Mestrado, Universidade de São Paulo, São Paulo.</span></span></span></td>
+<td valign="top" align="center">Aragaki</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">2001</td>
+<td valign="top" align="center">Aguiar <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e clímax</td>
+</tr>
+<tr>
+<td valign="top" align="left">2006</td>
+<td valign="top" align="center">Catharino <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left"><span class="ref"><sup class="xref xrefblue">2007</sup><span class="refCtt closed"><span>Polisel, R.T. &amp; Franco, G.A.D.C. 2007. Caracterização sucessional de uma floresta secundária com 40 anos de idade em Juquitiba, SP. Revista Brasileira de Biociências 5(supl. 2): 387-389.</span></span></span></td>
+<td valign="top" align="center">Polisel &amp; Franco</td>
+<td valign="top" align="center">Pioneira, secundária, tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left">2011</td>
+<td valign="top" align="center">Lima <i>et al</i>.</td>
+<td valign="top" align="center">Pioneira e não-pioneira</td>
+</tr>
+<tr>
+<td valign="top" align="left">2011</td>
+<td valign="top" align="center">Arzolla</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e umbrófila</td>
+</tr>
+<tr>
+<td valign="top" align="left">2013</td>
+<td valign="top" align="center">Barretto</td>
+<td valign="top" align="center">Pioneira, secundária inicial e secundária tardia</td>
+</tr>
+<tr>
+<td valign="top" align="left">2017</td>
+<td valign="top" align="center">Moura &amp; Mantovani</td>
+<td valign="top" align="center">Pioneira, secundária inicial, secundária tardia e sub-bosque</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet2" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 2</strong>    Composição florística nas três áreas amostradas (A, B e C), Parque Estadual da Cantareira, São Paulo, SP, Brasil. Class. Sucess.: Classificação Sucessional. PI: Pioneira, I: Secundária inicial, T: Secundária tardia, UM: Umbrófilas. Sindromes dispersão. ZOO: Zoocórica, ANE: Anemocórica, AUT: Autocórica.<br><strong>Table 2</strong>    Floristic composition of the three sampled areas (A, B and C), Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil. Class Sucess.: Succession Classification. PI: Pioneer, I: Early secondary, T: Late secondary, UM: Umbrophilous. Dispersion syndromes. ZOO: Zoochoric, ANE: Anemochoric, AUT: Autochoric.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th align="left">Família/Espécie</th>
+<th align="center">Nome Popular</th>
+<th align="center">Área A</th>
+<th align="center">Área B</th>
+<th align="center">Área C</th>
+<th align="center">Class. Sucess.</th>
+<th align="center">Class. Sucess. (P-NP)</th>
+<th align="center">Síndrome dispersão</th>
+<th align="center">Nº de coleta</th>
+</tr></thead>
+<tbody>
+<tr>
+<td align="left">Anacardiaceae <i>Schinus terebinthifolia</i> Raddi</td>
+<td align="center">aroeira-pimenteira</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">103</td>
+</tr>
+<tr>
+<td align="left">Annonaceae <i>Annona dolabripetala</i> Raddi</td>
+<td align="center">araticum</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">117</td>
+</tr>
+<tr>
+<td align="left">
+<i>Annona emarginata</i> (Schltdl.) H.Rainer</td>
+<td align="center">araticum-mirim</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">55</td>
+</tr>
+<tr>
+<td align="left">
+<i>Annona sylvatica</i> A.St.-Hil.</td>
+<td align="center">araticum-do-mato</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">59</td>
+</tr>
+<tr>
+<td align="left">Apocynaceae <i>Aspidosperma olivaceum</i> Müll.Arg.</td>
+<td align="center">guatambu</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">61</td>
+</tr>
+<tr>
+<td align="left">Arecaceae <i>Geonoma schottiana</i> Mart.</td>
+<td align="center">guaricanga</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">74</td>
+</tr>
+<tr>
+<td align="left">
+<i>Syagrus romanzoffiana</i> (Cham.) Glassman</td>
+<td align="center">jerivá</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">88</td>
+</tr>
+<tr>
+<td align="left">Asteraceae <i>Piptocarpha macropoda</i> (DC.) Baker</td>
+<td align="center">vassourão</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">97</td>
+</tr>
+<tr>
+<td align="left">Bignoniaceae <i>Jacaranda macrantha</i> Cham.</td>
+<td align="center">carobinha</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">118</td>
+</tr>
+<tr>
+<td align="left">Boraginaceae <i>Cordia sellowiana</i> Cham.</td>
+<td align="center">louro-mole</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">47</td>
+</tr>
+<tr>
+<td align="left">Burseraceae <i>Protium heptaphyllum</i> (Aubl.) Marchand</td>
+<td align="center">almecegueira</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">130</td>
+</tr>
+<tr>
+<td align="left">Cardiopteridaceae <i>Citronella paniculata</i> (Mart.) R.A.Howard</td>
+<td align="center">congonha</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">127</td>
+</tr>
+<tr>
+<td align="left">Caricaceae <i>Jacaratia heptaphylla </i>(Vell.) A.DC.</td>
+<td align="center">jaracatiá</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">106</td>
+</tr>
+<tr>
+<td align="left">Chrysobalanaceae <i>Hirtella hebeclada</i> Moric. ex DC.</td>
+<td align="center">vermelhão</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">58</td>
+</tr>
+<tr>
+<td align="left">Clusiaceae <i>Tovomitopsis paniculata</i> (Spreng.) Planch. &amp; Triana</td>
+<td align="center">azedinho</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">63</td>
+</tr>
+<tr>
+<td align="left">Cyatheaceae <i>Alsophila setosa</i> Kaulf.</td>
+<td align="center">samambaiaçu</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">57</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cyathea delgadii </i>Sternb.</td>
+<td align="center">samambaiaçu</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">123</td>
+</tr>
+<tr>
+<td align="left">Elaeocarpaceae <i>Sloanea guianensis</i> (Aubl.) Benth.</td>
+<td align="center">sapopemba</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">129</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sloanea hirsuta</i> (Schott) Planch. ex Benth.</td>
+<td align="center">ouriço-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">18</td>
+</tr>
+<tr>
+<td align="left">Euphorbiaceae <i>Alchornea triplinervia</i> (Spreng.) Müll.Arg.</td>
+<td align="center">tapiá-mirim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">13</td>
+</tr>
+<tr>
+<td align="left">
+<i>Croton floribundus</i> Spreng.</td>
+<td align="center">capixingui</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">93</td>
+</tr>
+<tr>
+<td align="left">
+<i>Croton macrobothrys</i> Baill.</td>
+<td align="center">sangra d´água</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">60</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sapium glandulosum</i> (L.) Morong</td>
+<td align="center">leiteiro</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">124</td>
+</tr>
+<tr>
+<td align="left">Fabaceae <i>Senegalia polyphylla</i> (DC.) Britton &amp; Rose</td>
+<td align="center">monjoleiro</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">108</td>
+</tr>
+<tr>
+<td align="left">
+<i>Bauhinia forficata</i> Link</td>
+<td align="center">pata-de-vaca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">95</td>
+</tr>
+<tr>
+<td align="left">
+<i>Copaifera trapezifolia</i> Hayne</td>
+<td align="center">copaiba-da-serra</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">121</td>
+</tr>
+<tr>
+<td align="left">
+<i>Dahlstedtia pinnata</i> (Benth.) Malme</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">AUT</td>
+<td align="center">92</td>
+</tr>
+<tr>
+<td align="left">
+<i>Inga sessilis</i> (Vell.) Mart.</td>
+<td align="center">ingá-ferradura</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">113</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mimosa scabrella</i> Benth.</td>
+<td align="center">bracatinga</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">05</td>
+</tr>
+<tr>
+<td align="left">
+<i>Piptadenia gonoacantha</i> (Mart.) J.F.Macbr.</td>
+<td align="center">pau-jacaré</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">AUT</td>
+<td align="center">102</td>
+</tr>
+<tr>
+<td align="left">
+<i>Platymiscium floribundum</i> Vogel</td>
+<td align="center">sacambú</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">53</td>
+</tr>
+<tr>
+<td align="left">Lauraceae <i>Cinnamomum hirsutum</i> (Lorea-Hern.) Van der Werff</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">125</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cinnamomum pseudoglaziovii</i> (Lorea-Hern.) Van der Werff</td>
+<td align="center">canela-garuva</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">23</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cryptocarya mandioccana</i> Meisn.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">56</td>
+</tr>
+<tr>
+<td align="left">
+<i>Endlicheria paniculata</i> (Spreng.) J.F.Macbr.</td>
+<td align="center">canela-cheirosa</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">04</td>
+</tr>
+<tr>
+<td align="left">
+<i>Nectandra membranacea</i> (Sw.) Griseb.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">107</td>
+</tr>
+<tr>
+<td align="left">
+<i>Nectandra oppositifolia</i> Nees</td>
+<td align="center">canela-ferrugem</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">33</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea glaziovii</i> Mez</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">132</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea catharinensis</i> Mez</td>
+<td align="center">canela-preta</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">52</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea koscinskii</i> Baitello &amp; Brotto</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">70</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea</i> aff. <i>montana</i> (Meisn.) Mez</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="left"></td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea puberula</i> (Rich.) Nees</td>
+<td align="center">canela-mole</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">105</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ocotea silvestris</i> Váttimo-Gil</td>
+<td align="center">canela-branca</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">86</td>
+</tr>
+<tr>
+<td align="left">Lecythidaceae <i>Cariniana estrellensis</i> (Raddi) Kuntze</td>
+<td align="center">jequitibá-branco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">82</td>
+</tr>
+<tr>
+<td align="left">Melastomataceae <i>Miconia budlejoides</i>Triana.</td>
+<td align="center">pixiririca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">116</td>
+</tr>
+<tr>
+<td align="left">
+<i>Miconia cinnamomifolia</i> (DC.) Naudin</td>
+<td align="center">jacatirão</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">11</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mouriri chamissoana</i> Cogn.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">31</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pleroma granulosum</i> (Desr.) D. Don</td>
+<td align="center">quaresmeira</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">101</td>
+</tr>
+<tr>
+<td align="left">Meliaceae <i>Cabralea canjerana</i> (Vell.) Mart.</td>
+<td align="center">canjerana</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">32</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cedrela fissilis</i> Vell.</td>
+<td align="center">cedro rosa</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">89</td>
+</tr>
+<tr>
+<td align="left">
+<i>Guarea macrophylla</i> Vahl ssp. <i>tuberculata</i> (Vell.) T.D.Penn.</td>
+<td align="center">marinheiro</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">24</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia pallens</i> C.DC.</td>
+<td align="center">catiguá</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">79</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia silvatica</i> C.DC.</td>
+<td align="center">catiguá</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">16</td>
+</tr>
+<tr>
+<td align="left">Monimiaceae <i>Mollinedia elegans</i> Tul.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">48</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia schottiana</i> (Spreng.) Perkins</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">01</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia triflora</i> (Spreng.) Tul.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">131</td>
+</tr>
+<tr>
+<td align="left">
+<i>Mollinedia uleana</i> Perkins</td>
+<td align="center">capixim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">64</td>
+</tr>
+<tr>
+<td align="left">Moraceae <i>Ficus luschnathiana</i> (Miq.) Miq.</td>
+<td align="center">figueira-branca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">03</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sorocea bonplandii</i> (Baill.) W.C.Burger et al.</td>
+<td align="center">canxim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">51</td>
+</tr>
+<tr>
+<td align="left">Myristicaceae <i>Virola bicuhyba</i> (Schott ex Spreng.) Warb.</td>
+<td align="center">bicuíba</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">12</td>
+</tr>
+<tr>
+<td align="left">Myrtaceae <i>Eugenia beaurepaireana</i> (Kiaersk.) D.Legrand</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">90</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia cerasiflora</i> Miq.</td>
+<td align="center">guamirim</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">38</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia cereja</i> D.Legrand</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">62</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia involucrata</i> DC.</td>
+<td align="center">cereja-do-rio-grande</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">68</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia prasina</i> O.Berg</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">20</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia subterminalis</i> DC.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">19</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia supraaxillaris</i> Spring</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">77</td>
+</tr>
+<tr>
+<td align="left">
+<i>Marlierea racemosa</i> (Vell.) Kiaersk.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">65</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia anacardiifolia</i> Gardner</td>
+<td align="center">marmelinho</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">45</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia hebepetala</i> DC.</td>
+<td align="center">guamirim</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">119</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia neobrasiliensis</i> A.R.Lourenço &amp; E.Lucas</td>
+<td align="center">araçarana</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">49</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia neolucida</i> A.R.Lourenço &amp; E.Lucas</td>
+<td align="center">araçarana</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">28</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia splendens</i> (Sw.) DC.</td>
+<td align="center">guamirim</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">54</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tenuivenosa</i> Kiaersk.</td>
+<td align="center">cambuí</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">91</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tijucensis</i> Kiaersk.</td>
+<td align="center">guamirim-ferro</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">84</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia tomentosa</i> (Aubl.) DC.</td>
+<td align="center">goiaba-brava</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">39</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrcia</i> sp.</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">54</td>
+</tr>
+<tr>
+<td align="left">Nyctaginaceae <i>Guapira opposita</i> (Vell.) Reitz</td>
+<td align="center">maria-mole</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">08</td>
+</tr>
+<tr>
+<td align="left">Olacaceae <i>Heisteria silvianii</i> Schwacke</td>
+<td align="center">brinco-de-mulata</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">14</td>
+</tr>
+<tr>
+<td align="left">Oleaceae <i>Chionanthus filiformis</i> (Vell.) P.S.Green</td>
+<td align="center">azeitona-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">35</td>
+</tr>
+<tr>
+<td align="left">Peraceae <i>Pera glabrata</i> (Schott) Baill.</td>
+<td align="center">cabeluda-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">120</td>
+</tr>
+<tr>
+<td align="left">Phyllantaceae <i>Hyeronima alchorneoides</i> Allemão</td>
+<td align="center">urucuruna</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">100</td>
+</tr>
+<tr>
+<td align="left">Phytolaccaceae <i>Seguieria langsdorffii</i> Moq.</td>
+<td align="center">limoeiro-do-mato</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">112</td>
+</tr>
+<tr>
+<td align="left">Picramniaceae <i>Picramnia glazioviana</i> Engl.</td>
+<td align="center">cafezinho</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">30</td>
+</tr>
+<tr>
+<td align="left">Polygonaceae <i>Ruprechtia laxiflora</i> Meisn.</td>
+<td align="center">marmeleiro-do-mato</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">115</td>
+</tr>
+<tr>
+<td align="left">Primulaceae <i>Myrsine gardneriana</i> A.DC.</td>
+<td align="center">capororoca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">109</td>
+</tr>
+<tr>
+<td align="left">
+<i>Myrsine umbellata</i> Mart.</td>
+<td align="center">capororoca</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">110</td>
+</tr>
+<tr>
+<td align="left">Proteaceae <i>Euplassa cantareirae</i> Sleumer</td>
+<td align="center">carvalho-da-cantareira</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">50</td>
+</tr>
+<tr>
+<td align="left">Rosaceae <i>Prunus myrtifolia</i> (L.) Urb.</td>
+<td align="center">pessegueiro-bravo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">17</td>
+</tr>
+<tr>
+<td align="left">Rubiaceae <i>Cordiera myrciifolia</i> (K.Schum.) CHPerss &amp; Delprete</td>
+<td align="center">marmelinho</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">87</td>
+</tr>
+<tr>
+<td align="left">
+<i>Posoqueria latifolia</i> (Rudge) Schult.</td>
+<td align="center">baga-de-macaco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">66</td>
+</tr>
+<tr>
+<td align="left">
+<i>Psychotria suterella</i> Müll.Arg.</td>
+<td align="center">pasto-d’anta</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">22</td>
+</tr>
+<tr>
+<td align="left">
+<i>Psychotria vellosiana</i> Benth.</td>
+<td align="center">erva-de-rato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">46</td>
+</tr>
+<tr>
+<td align="left">
+<i>Rudgea gardenioides</i> (Cham.) Müll.Arg.</td>
+<td align="center">jasmim-do-mato</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">122</td>
+</tr>
+<tr>
+<td align="left">Rutaceae <i>Esenbeckia grandiflora</i> Mart.</td>
+<td align="center">pau-de-cutia</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">AUT</td>
+<td align="center">67</td>
+</tr>
+<tr>
+<td align="left">Salicaceae <i>Casearia decandra</i> Jacq.</td>
+<td align="center">guaçatonga</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">83</td>
+</tr>
+<tr>
+<td align="left">
+<i>Casearia obliqua</i> Spreng.</td>
+<td align="center">guaçatonga</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">69</td>
+</tr>
+<tr>
+<td align="left">
+<i>Casearia sylvestris</i> Sw.</td>
+<td align="center">erva de lagarto</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">94</td>
+</tr>
+<tr>
+<td align="left">Sapindaceae <i>Allophylus petiolulatus</i> Radlk.</td>
+<td align="center">fruta-de-pombo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">73</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cupania oblongifolia</i> Mart.</td>
+<td align="center">cuvantã</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">09</td>
+</tr>
+<tr>
+<td align="left">
+<i>Matayba elaeagnoides</i> Radlk.</td>
+<td align="center">camboatá-branco</td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">76</td>
+</tr>
+<tr>
+<td align="left">
+<i>Matayba guianensis</i> Aubl.</td>
+<td align="center">camboatá-branco</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">85</td>
+</tr>
+<tr>
+<td align="left">Sapotaceae <i>Chrysophyllum inornatum</i> Mart.</td>
+<td align="center">aleixo</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">75</td>
+</tr>
+<tr>
+<td align="left">
+<i>Ecclinusa ramiflora</i> Mart.</td>
+<td align="center">guacá</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">111</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pouteria bullata</i> (S.Moore) Baehni</td>
+<td align="center">guapeva</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">114</td>
+</tr>
+<tr>
+<td align="left">Solanaceae <i>Cestrum schlechtendalii</i>. G.Don.</td>
+<td align="center">coerana</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">126</td>
+</tr>
+<tr>
+<td align="left">
+<i>Sessea brasiliensis</i> Toledo</td>
+<td align="center">peroba-d’água</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ANE</td>
+<td align="center">98</td>
+</tr>
+<tr>
+<td align="left">
+<i>Solanum pseudoquina</i> A.St.-Hil.</td>
+<td align="center">quina-falsa</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">128</td>
+</tr>
+<tr>
+<td align="left">Symplocaceae <i>Symplocos variabilis</i> Mart. ex Miq.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">UM</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">71</td>
+</tr>
+<tr>
+<td align="left">Thymelaeaceae <i>Daphnopsis fasciculata</i> (Meisn.) Nevling</td>
+<td align="center">embira-branca</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">T</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">82</td>
+</tr>
+<tr>
+<td align="left">Urticaceae <i>Urera baccifera</i> (L.) Gaudich. ex Wedd.</td>
+<td align="center">urtiga</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">96</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cecropia glaziovii</i> Snethl.</td>
+<td align="center">embaúba-vermelha</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">PI</td>
+<td align="center">P</td>
+<td align="center">ZOO</td>
+<td align="center">104</td>
+</tr>
+<tr>
+<td align="left">
+<i>Coussapoa microcarpa</i> (Schott) Rizzini</td>
+<td align="center">mata-pau</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="left"></td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ZOO</td>
+<td align="center">10</td>
+</tr>
+<tr>
+<td align="left">Vochysiaceae <i>Vochysia magnifica</i> Warm.</td>
+<td align="center">guaricica</td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">07</td>
+</tr>
+<tr>
+<td align="left">
+<i>Vochysia selloi</i> Warm.</td>
+<td align="left"></td>
+<td align="left"></td>
+<td align="center">X</td>
+<td align="center">X</td>
+<td align="center">I</td>
+<td align="center">NP</td>
+<td align="center">ANE</td>
+<td align="center">78</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet3" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 3</strong>    Parâmetros com valores totais e por área, Parque Estadual da Cantareira, São Paulo, SP, Brasil.<br><strong>Table 3</strong>    Parameters with total values and by area, Parque Estadual da Cantareira, São Paulo, São Paulo State, Brasil.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead><tr>
+<th valign="bottom" align="left">Parâmetros</th>
+<th align="center">Valores Totais</th>
+<th align="center">Área A</th>
+<th align="center">Área B</th>
+<th align="center">Área C</th>
+</tr></thead>
+<tbody>
+<tr>
+<td valign="bottom" align="left">Nº de indivíduos</td>
+<td align="center">1020</td>
+<td align="center">321</td>
+<td align="center">399</td>
+<td align="center">300</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Nº de espécies</td>
+<td align="center">115</td>
+<td align="center">54</td>
+<td align="center">68</td>
+<td align="center">56</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Nº de famílias</td>
+<td align="center">45</td>
+<td align="center">26</td>
+<td align="center">32</td>
+<td align="center">30</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Densidade (ind./ha)</td>
+<td align="center">1700</td>
+<td align="center">1605</td>
+<td align="center">1995</td>
+<td align="center">1500</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Área basal total (m<sup>2</sup>)</td>
+<td align="center">23,88</td>
+<td align="center">9,079</td>
+<td align="center">8,677</td>
+<td align="center">6,124</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Dominância (m<sup>2</sup>/ha)</td>
+<td align="center">39,801</td>
+<td align="center">45,396</td>
+<td align="center">43,385</td>
+<td align="center">30,622</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Indice Shannon-Wiener</td>
+<td align="center">3,82</td>
+<td align="center">3,27</td>
+<td align="center">3,55</td>
+<td align="center">3,42</td>
+</tr>
+<tr>
+<td valign="bottom" align="left">Equabilidade</td>
+<td align="center">0,805</td>
+<td align="center">0,797</td>
+<td align="center">0,84</td>
+<td align="center">0,82</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalTables" id="ModalTablet4" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog modal-lg"><div class="modal-content">
+<div class="modal-header">
+<button type="button" class="close" data-dismiss="modal"><span aria-hidden="true">×</span><span class="sr-only">Close</span></button><h4 class="modal-title">
+<span class="sci-ico-fileTable"></span><strong>Tabela 4</strong>    Lista de espécies ameaçadas e sua classificação nas listas de <span class="ref"><strong class="xref xrefblue">São Paulo (2016)</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brasil (2019c) e IUCN (2019). Categorias VU: Vulnerável, EN: Em perigo e EX: Extinta.<br><strong>Table 4</strong>    List of threatened species and their classification in the lists of <span class="ref"><strong class="xref xrefblue">São Paulo, 2016</strong><span class="refCtt closed"><span>São Paulo. 2016. Resolução SMA nº 057, de 05 de junho de 2016. Publica a segunda revisão da lista oficial das espécies da flora ameaçadas de extinção no Estado de São Paulo. Diário Oficial do Estado de São Paulo, de 30/06/2016, Seção 1, pp. 55-57.</span></span></span>, Brazil, 2019c and IUCN, 2019. VU categories: Vulnerable, EN: Endangered and EX: Extinct.<br>
+</h4>
+</div>
+<div class="modal-body"><div class="table table-hover"><table>
+<thead>
+<tr>
+<th rowspan="2" align="left">Espécie</th>
+<th align="left"></th>
+<th align="center">Listas</th>
+<th align="left"></th>
+</tr>
+<tr>
+<th align="center">São Paulo</th>
+<th align="center">Brasil</th>
+<th align="center">IUCN</th>
+</tr>
+</thead>
+<tbody>
+<tr>
+<td align="left">
+<i>Ocotea catharinensis</i> Mez</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Cedrela fissilis</i> Vell.</td>
+<td align="center">VU</td>
+<td align="center">VU</td>
+<td align="center">EN</td>
+</tr>
+<tr>
+<td align="left">
+<i>Trichilia silvatica</i> C.DC.</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Virola bicuhyba</i> (Schott ex Spreng.) Warb.</td>
+<td align="center">EN</td>
+<td align="center">EN</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">
+<i>Eugenia prasina</i> O.Berg</td>
+<td align="center">-</td>
+<td align="center">-</td>
+<td align="center">VU</td>
+</tr>
+<tr>
+<td align="left">
+<i>Euplassa cantareirae</i> Sleumer</td>
+<td align="center">EX</td>
+<td align="center">EN</td>
+<td align="center">-</td>
+</tr>
+<tr>
+<td align="left">
+<i>Pouteria bullata</i> (S.Moore) Baehni</td>
+<td align="center">EN</td>
+<td align="center">EN</td>
+<td align="center">VU</td>
+</tr>
+</tbody>
+</table></div></div>
+<div class="modal-footer"></div>
+</div></div></div>
+<div class="modal fade ModalDefault" id="ModalArticles" tabindex="-1" role="dialog" aria-hidden="true"><div class="modal-dialog"><div class="modal-content">
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