The surveyvoi package is a decision support tool for prioritizing sites for ecological surveys based on their potential to improve plans for conserving biodiversity (e.g. plans for establishing protected areas). Given a set of sites that could potentially be acquired for conservation management – wherein some sites have previously been surveyed and other sites have not – this package provides functionality to generate and evaluate plans for additional surveys. Specifically, plans for ecological surveys can be generated using various conventional approaches (e.g. maximizing expected species richness, geographic coverage, diversity of sampled environmental conditions) and by maximizing value of information. After generating plans for surveys, they can also be evaluated using value of information analysis. Please note that several functions depend on the Gurobi optimization software (available from https://www.gurobi.com). Additionally, the JAGS software (available from https://mcmc-jags.sourceforge.io/) is required to fit hierarchical generalized linear models.
The latest official version can be installed from the Comprehensive R Archive Network (CRAN) using the following R code.
install.packages("surveyvoi", repos = "https://cran.rstudio.com/")
Alternatively, the latest development version can be installed from GitHub using the following code. Please note that while developmental versions may contain additional features not present in the official version, they may also contain coding errors.
if (!require(remotes)) install.packages("remotes")
remotes::install_github("prioritizr/surveyvoi")
The Rtools software needs to be installed to install the surveyvoi R package from source. This software provides system requirements from rwinlib.
The gmp
, fftw3
, mpfr
, and symphony
libraries need to be
installed to install the surveyvoi R package. Although the fftw3
and
symphony
libraries are not used directly, they are needed to
successfully install dependencies. For recent versions of Ubuntu (18.04
and later), these libraries are available through official repositories.
They can be installed using the following system commands:
apt-get -y update
apt-get install -y libgmp3-dev libfftw3-dev libmpfr-dev coinor-libsymphony-dev
For Unix-alikes, gmp
(>= 4.2.3), mpfr
(>= 3.0.0), fftw3
(>=
3.3), and symphony
(>= 5.6.16) are required.
The gmp
, fftw
, mpfr
, and symphony
libraries are required.
Although the fftw3
and symphony
libraries are not used directly,
they are needed to successfully install dependencies. The easiest way to
install these libraries is using HomeBrew. After
installing HomeBrew, these libraries can be installed using the
following commands in the system terminal:
brew tap coin-or-tools/coinor
brew install symphony
brew install pkg-config
brew install gmp
brew install fftw
brew install mpfr
Please cite the surveyvoi R package when using it in publications. To cite the package, please use:
Hanson, JO, McCune JL, Chadès I, Proctor CA, Hudgins EJ, & Bennett JR (2023) Optimizing ecological surveys for conservation. Journal of Applied Ecology, 60: 41–51. Available at https://doi.org/10.1111/1365-2664.14309.
Here we provide a short example showing how to use the surveyvoi R package to prioritize funds for ecological surveys. In this example, we will generate plans for conducting ecological surveys (termed “survey schemes”) using simulated data for six sites and three conservation features (e.g. bird species). To start off, we will set the seed for the random number generator for reproducibility and load some R packages.
set.seed(502) # set RNG for reproducibility
library(surveyvoi) # package for value of information analysis
library(dplyr) # package for preparing data
library(tidyr) # package for preparing data
library(ggplot2) # package for plotting data
Now we will load some datasets that are distributed with the package.
First, we will load the sim_sites
object. This spatially explicit
dataset (i.e. sf
object) contains information on the sites within our
study area. Critically, it contains (i) sites that have already been
surveyed, (ii) candidate sites for additional surveys, (iii) sites that
have already been protected, and (iv) candidate sites that could be
protected in the future. Each row corresponds to a different site, and
each column describes different properties associated with each site. In
this table, the "management_cost"
column indicates the cost of
protecting each site; "survey_cost"
column indicates the cost of
conducting an ecological survey within each site; and "e1"
and "e2"
columns contain environmental data for each site (not used in this
example). The remaining columns describe the existing survey data and
the spatial distribution of the features across the sites. The "n1"
,
"n2"
, and "n3"
columns indicate the number of surveys conducted
within each site that looked for each of the three features
(respectively); and "f1"
, "f2"
, and "f3"
columns describe the
proportion of surveys within each site that looked for each feature
where the feature was detected (respectively). For example, if "n1"
has a value of 2 and "f1"
has a value of 0.5 for a given site, then
the feature "f1"
was detected in only one of the two surveys conducted
in this site that looked for the feature. Finally, the "p1"
, "p2"
,
and "p3"
columns contain modeled probability estimates of each species
being present in each site (see fit_hglm_occupancy_models()
and
fit_xgb_occupancy_models()
to generate such estimates for your own
data).
# load data
data(sim_sites)
# print table
print(sim_sites, width = Inf)
## Simple feature collection with 6 features and 13 fields
## Geometry type: POINT
## Dimension: XY
## Bounding box: xmin: 0.02541313 ymin: 0.07851093 xmax: 0.9888107 ymax: 0.717068
## CRS: NA
## # A tibble: 6 × 14
## survey_cost management_cost f1 f2 f3 n1 n2 n3 e1 e2
## <dbl> <dbl> <dbl> <dbl> <dbl> <dbl> <dbl> <dbl> <dbl> <dbl>
## 1 19 99 0 0 0 0 0 0 1.13 0.535
## 2 22 87 0 1 0.25 4 4 4 -1.37 -1.45
## 3 13 94 1 1 0 1 1 1 0.155 -0.867
## 4 19 61 0 0 0 0 0 0 -0.792 1.32
## 5 9 105 0 0 0 0 0 0 -0.194 0.238
## 6 12 136 0 0 0 0 0 0 1.07 0.220
## p1 p2 p3 geometry
## <dbl> <dbl> <dbl> <POINT>
## 1 0.999 0.988 0.21 (0.03529733 0.544939)
## 2 0.001 0.995 0.152 (0.33276 0.3174416)
## 3 0.966 1 0.017 (0.6141922 0.07851093)
## 4 0 0 1 (0.02541313 0.1147132)
## 5 0.11 0.006 0.831 (0.9888107 0.2152785)
## 6 1 1 0.082 (0.9038749 0.717068)
# plot cost of protecting each site
ggplot(sim_sites) +
geom_sf(aes(color = management_cost), size = 4) +
ggtitle("management_cost") +
theme(legend.title = element_blank(), text = element_text(size = 16))
# plot cost of conducting an additional survey in each site
# note that these costs are much lower than the protection costs
ggplot(sim_sites) +
geom_sf(aes(color = survey_cost), size = 4) +
ggtitle("survey_cost") +
theme(legend.title = element_blank(), text = element_text(size = 16))
# plot survey data
## n1, n2, n3: number of surveys in each site that looked for each feature
sim_sites %>%
select(n1, n2, n3) %>%
gather(name, value, -geometry) %>%
ggplot() +
geom_sf(aes(color = value), size = 4) +
facet_wrap(~name, nrow = 1) +
theme(text = element_text(size = 16))
# plot survey results
## f1, f2, f3: proportion of surveys in each site that looked for each feature
## that detected the feature
sim_sites %>%
select(f1, f2, f3) %>%
gather(name, value, -geometry) %>%
ggplot() +
geom_sf(aes(color = value), size = 4) +
facet_wrap(~name, nrow = 1) +
scale_color_continuous(limits = c(0, 1)) +
theme(text = element_text(size = 16))
# plot modeled probability of occupancy data
sim_sites %>%
select(p1, p2, p3) %>%
gather(name, value, -geometry) %>%
ggplot() +
geom_sf(aes(color = value), size = 4) +
facet_wrap(~name, nrow = 1) +
scale_color_continuous(limits = c(0, 1)) +
theme(text = element_text(size = 16))
Next, we will load the sim_features
object. This table contains
information on the conservation features (e.g. species). Specifically,
each row corresponds to a different feature, and each column contains
information associated with the features. In this table, the "name"
column contains the name of each feature; "survey"
column indicates
whether future surveys would look for this species;
"survey_sensitivity"
and "survey_specificity"
columns denote the
sensitivity (true positive rate) and specificity (true negative rate)
for the survey methodology for correctly detecting the feature;
"model_sensitivity"
and "model_specificity"
columns denote the
sensitivity (true positive rate) and specificity (true negative rate)
for the species distribution models fitted for each feature; and
"target"
column denotes the required number of protected sites for
each feature (termed “representation target”, each feature has a target
of 2 site).
# load data
data(sim_features)
# print table
print(sim_features, width = Inf)
## # A tibble: 3 × 7
## name survey survey_sensitivity survey_specificity model_sensitivity
## <chr> <lgl> <dbl> <dbl> <dbl>
## 1 f1 TRUE 0.951 0.854 0.711
## 2 f2 TRUE 0.990 0.832 0.722
## 3 f3 TRUE 0.986 0.808 0.772
## model_specificity target
## <dbl> <dbl>
## 1 0.841 2
## 2 0.806 2
## 3 0.871 2
After loading the data, we will now generate an optimized ecological
survey scheme. To achieve this, we will use
approx_optimal_survey_scheme()
function. This function uses a greedy
heuristic algorithm to maximize value of information. Although other
functions can return solutions that are guaranteed to be optimal
(i.e. optimal_survey_scheme()
), they can take a very long time to
complete because they use a brute-force approach. This function also
uses an approximation routine to reduce computational burden.
To perform the optimization, we will set a total budget for (i) protecting sites and (ii) surveying sites. Although you might be hesitant to specify a budget, please recall that you would make very different plans depending on available funds. For instance, if you have near infinite funds then you wouldn’t bother conducting any surveys and simply protect everything. Similarly, if you had very limited funds, then you wouldn’t survey any sites to ensure that at least one site could be protected. Generally, conservation planning problems occur somewhere between these two extremes—but the optimization process can’t take that into account if you don’t specify a budget. For brevity, here we will set the total budget as 90% of the total costs for protecting sites.
# calculate budget
budget <- sum(0.4 * sim_sites$management_cost)
# generate optimized survey scheme
opt_scheme <-
approx_optimal_survey_scheme(
site_data = sim_sites,
feature_data = sim_features,
site_detection_columns = c("f1", "f2", "f3"),
site_n_surveys_columns = c("n1", "n2", "n3"),
site_probability_columns = c("p1", "p2", "p3"),
site_management_cost_column = "management_cost",
site_survey_cost_column = "survey_cost",
feature_survey_column = "survey",
feature_survey_sensitivity_column = "survey_sensitivity",
feature_survey_specificity_column = "survey_specificity",
feature_model_sensitivity_column = "model_sensitivity",
feature_model_specificity_column = "model_specificity",
feature_target_column = "target",
total_budget = budget,
survey_budget = budget,
verbose = TRUE
)
# the opt_scheme object is a matrix that contains the survey schemes
# each column corresponds to a different site,
# and each row corresponds to a different solution
# in the event that there are multiple near-optimal survey schemes, then this
# matrix will have multiple rows
print(str(opt_scheme))
## logi [1, 1:6] TRUE FALSE FALSE TRUE TRUE FALSE
## - attr(*, "ev")= num [1, 1:100] 0.596 0.596 0.596 0.596 0.596 ...
## NULL
# let's add the first solution (row) in opt_scheme to the site data to plot it
sim_sites$scheme <- c(opt_scheme[1, ])
# plot scheme
# TRUE = selected for an additional ecological survey
# FALSE = not selected
ggplot(sim_sites) +
geom_sf(aes(color = scheme), size = 4) +
ggtitle("scheme") +
theme(text = element_text(size = 16))
This has just been a taster of the surveyvoi R package. In addition to this functionality, it can be used to evaluate survey schemes using value of information analysis. Furthermore, it can be used to generate survey schemes using conventional approaches (e.g. sampling environmental gradients, and selecting places with highly uncertain information). For more information, see the package vignette.
If you have any questions about using the surveyvoi R package or suggestions for improving it, please file an issue at the package’s online code repository.