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admahood committed Nov 29, 2022
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2 changes: 1 addition & 1 deletion Appendix_figures.Rmd
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# Appendix S1 for: "Fuel connectivity, burn severity, and seedbank survivorship drive ecosystem transformation in a semi-arid shrubland."

<!-- -Submitted to *Ecology* -->
-Submitted to *Ecology*

Adam L. Mahood^1,2,3,`*`^, Michael J. Koontz^2^, Jennifer K. Balch^1,2,4^

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16 changes: 16 additions & 0 deletions Appendix_figures.tex
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\setlength{\itemsep}{0pt}\setlength{\parskip}{0pt}}
\setcounter{secnumdepth}{-\maxdimen} % remove section numbering
\newcommand{\beginsupplement} {\renewcommand{\thetable}{S\arabic{table}} \setcounter{table}{0} \renewcommand{\thefigure}{S\arabic{figure}}}
\usepackage{booktabs}
\usepackage{longtable}
\usepackage{array}
\usepackage{multirow}
\usepackage{wrapfig}
\usepackage{float}
\usepackage{colortbl}
\usepackage{pdflscape}
\usepackage{tabu}
\usepackage{threeparttable}
\usepackage{threeparttablex}
\usepackage[normalem]{ulem}
\usepackage{makecell}
\usepackage{xcolor}
\ifLuaTeX
\usepackage{selnolig} % disable illegal ligatures
\fi
Expand All @@ -75,6 +89,8 @@ \section{Appendix S1 for: ``Fuel connectivity, burn severity, and
seedbank survivorship drive ecosystem transformation in a semi-arid
shrubland.''}\label{appendix-s1-for-fuel-connectivity-burn-severity-and-seedbank-survivorship-drive-ecosystem-transformation-in-a-semi-arid-shrubland.}}

-Submitted to \emph{Ecology}

Adam L. Mahood\textsuperscript{1,2,3,\texttt{*}}, Michael J.
Koontz\textsuperscript{2}, Jennifer K. Balch\textsuperscript{1,2,4}

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9 changes: 6 additions & 3 deletions R/conceptual_figure.R
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Expand Up @@ -176,10 +176,13 @@ ph3 <- ggsem(pm_h3,


p_final<- ggarrange(ph1, ph2, ph3, ph2a, ph2b, make_legend(), nrow=2, ncol=3)

extrafont::loadfonts()
ggsave(plot = p_final,
filename = "images/conceptual_figure.png",
bg="white", height=11, width=17)
bg="white", height=11, width=17, dpi=600)
ggsave(plot = p_final,
filename = "images/conceptual_figure.jpg",
bg="white", height=11, width=17, dpi=600)
ggsave(plot = p_final,
filename = "images/conceptual_figure.pdf",
filename = "images/conceptual_figure.png",
bg="white", height=11, width=17)
3 changes: 2 additions & 1 deletion R/ggplot_sem_sb.R
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Expand Up @@ -154,7 +154,8 @@ ggsem <- function(fit, filename, title="Path Model",layout_df = NA, rename_nodes
theme(#plot.title = element_text(size = 30),
legend.position = "none",
plot.background = element_rect(color="black", fill="transparent")
)
)+
theme_graph(base_family = 'Helvetica')
if(length(title) ==1)p1 <- p1 + ggtitle(title[1]) else p1 <- p1 + ggtitle(title[1], title[2])
if(rename_nodes){ p1 <- p1 + geom_node_text(aes(label = new_node_names_df$new_names),
fontface = "bold",
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2 changes: 1 addition & 1 deletion R/make_appendix.R
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Expand Up @@ -11,7 +11,7 @@ rmarkdown::render("Appendix_tables.Rmd")
x=date()
x=strsplit(x," ")[[1]]

system("pdftk Appendix_figures.pdf Appendix_tables.pdf cat output Appendix_S1_preprint.pdf")
system("pdftk Appendix_figures.pdf Appendix_tables.pdf cat output Appendix_S1.pdf")

# make full paper

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23,548 changes: 23,548 additions & 0 deletions data/blm_aim/BLM_Natl_AIM_TerrADat_Hub_2022.csv

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62 changes: 14 additions & 48 deletions sb_manuscript.Rmd

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49 changes: 10 additions & 39 deletions sb_manuscript.tex
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\normalsize

Open Research Statement: Data and code to recreate the analysis are
freely available at \url{https://doi.org/10.5281/zenodo.5293996}.
Open Research Statement: All data and code used in the analysis are
freely available at \url{https://doi.org/10.5281/zenodo.5293996}. The
Bureau of Land Management's Assessment, Inventory and Monitoring
TerrADat dataset is available at version is available at:
\url{https://blm-gbp-hub-blm-egis.hub.arcgis.com/}

\newpage

Expand Down Expand Up @@ -423,7 +426,7 @@ \subsection{2. Methods}\label{methods}}
\emph{2.1 Study Area}

The study was conducted in north-central Nevada the day after a large
fire (the Hot Pot Fire) was extinguished (Appendix S1, Fig. S1). The Hot
fire (the Hot Pot Fire) was extinguished (Appendix S1: Fig. S1). The Hot
Pot Fire burned just over 50,000 hectares in less than a week. The
pre-fire landcover was predominantly \emph{B. tectorum} and Wyoming big
sagebrush plant communities. The fire occurred after the early season
Expand Down Expand Up @@ -626,7 +629,7 @@ \subsection{3. Results}\label{results}}

We found support for each hypothesized component of the positive
feedback loop independently and when combined in the path model
(\(\chi^2\) = 3.17, p = 0.39, Figure 4a, Appendix S1, Tables S4 \& S5).
(\(\chi^2\) = 3.17, p = 0.39, Figure 4a, Appendix S1: Tables S4 \& S5).
For H1, TVC had a weak positive relationship with burn severity
(\(\beta\) = 2.4, p = 0.083, R\(^2\) = 0.27, Figure 4b, Appendix S1:
Table S2). For our remotely sensed analysis, Green NDVI, NDSVI and their
Expand Down Expand Up @@ -731,10 +734,10 @@ \subsection{4. Discussion}\label{discussion}}
provide enough niche compartmentalization to allow native plants to
persist in spite of the invasion prior to fire occurrence. Three years
after fire, almost all of the sites were dominated by introduced
annuals, and lacked any structural heterogeneity (Appendix S1, Fig.
annuals, and lacked any structural heterogeneity (Appendix S1: Fig.
S6c). Thus native plants may have been able to persist via niche
compartmentalization after the initial invasion, but fire burned away
most of the seeds (Appendix S1, Fig. S3, S7) and removed all of the
most of the seeds (Appendix S1: Fig. S3, S7) and removed all of the
structural benefits, and microclimatic refugia that shrub cover
provides. In this clean slate post-fire environment, the altered species
composition of the seedbank and superior post-fire dispersal of \emph{B.
Expand Down Expand Up @@ -817,7 +820,7 @@ \subsection{4. Discussion}\label{discussion}}
this system is controlled by measurable fire properties and ecosystem
structural components. We found that annual grass cover was not the
single variable that explained burn severity and fuel connectivity
(Appendix S1, Fig S5). Rather, it was the contribution of annual grass
(Appendix S1: Fig S5). Rather, it was the contribution of annual grass
cover to the total connectivity of the system (Figure 2). The most
important areas to prioritize for management interventions could
paradoxically be areas with relatively low levels of annual grass cover
Expand Down Expand Up @@ -1682,36 +1685,4 @@ \subsection{Figure Captions}\label{figure-captions}}
depth, aspect, elevation and pre-fire diversity. Black line is the mean
prediction, each colored line represents one posterior sample.

\newpage

\begin{figure}
\centering
\includegraphics[width=0.75\textwidth,height=\textheight]{images/burnsev_fig.pdf}
\caption{.}
\end{figure}

\newpage

\begin{figure}
\centering
\includegraphics{images/fig2_seed_bank.pdf}
\caption{.}
\end{figure}

\newpage

\begin{figure}
\centering
\includegraphics{images/conceptual_figure.png}
\caption{.}
\end{figure}

\newpage

\begin{figure}
\centering
\includegraphics{images/big_plot_v2.pdf}
\caption{.}
\end{figure}

\end{document}
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