nocite: | @Daru2020, @Daru2017
phyloregion
is available from the Comprehensive R Archive Network, so you can use the following line of code to install and run it:
install.packages("phyloregion")
Alternatively, you can install the development version of phyloregion
hosted
on GitHub. To do this, you will need to install the devtools
package. In R, type:
if (!requireNamespace("remotes", quietly = TRUE)) install.packages("remotes") remotes::install_github("darunabas/phyloregion")
When installed, load the package in R:
library(phyloregion)
phyloregion
The workflow of the phyloregion
package demonstrates steps from preparation
of different types of data to visualizing the results of biogeographical regionalization, together with tips on selecting the optimal method for
achieving the best output, depending on the types of data used and research questions.
In R, phylogenetic relationships among species / taxa are often represented as a phylo
object implemented in the ape
package[@Paradis2018]. Phylogenies (often in the Newick
or Nexus formats) can be imported into R with the read.tree
or read.nexus
functions of the ape
package[@Paradis2018].
library(ape) library(Matrix) library(terra) data(africa) sparse_comm <- africa$comm tree <- africa$phylo tree <- keep.tip(tree, intersect(tree$tip.label, colnames(sparse_comm))) par(mar=c(2,2,2,2)) plot(tree, show.tip.label=FALSE)
The phyloregion
package has functions for manipulating three kinds of distribution
data: point records, vector polygons and raster layers. An overview can be easily obtained with the functions points2comm
, polys2comm
and rast2comm
for point records, polygons, or raster layers, respectively. Depending on the data source, all three functions ultimately provide convenient interfaces to convert the distribution data to a community matrix at varying spatial grains and extents for downstream analyses.
We will play around with these functions in turn.
points2comm
Here, we will generate random points in geographic space, similar to occurrence data obtained from museum records, GBIF, iDigBio, or CIESIN which typically have columns of geographic coordinates for each observation.
s <- vect(system.file("ex/nigeria.json", package="phyloregion")) set.seed(1) m <- as.data.frame(spatSample(s, 1000, method = "random"), geom = "XY")[-1] names(m) <- c("lon", "lat") species <- paste0("sp", sample(1:100)) m$taxon <- sample(species, size = nrow(m), replace = TRUE) pt <- points2comm(dat = m, res = 0.5, lon = "lon", lat = "lat", species = "taxon") # This generates a list of two objects head(pt[[1]][1:5, 1:5])
polys2comm
This function converts polygons to a community matrix at varying spatial grains and extents for downstream analyses. Polygons can be derived from the IUCN Redlist spatial database (https: //www.iucnredlist.org/resources/spatial-data-download), published monographs or field guides validated by taxonomic experts. To illustrate this function, we will use the function random_species
to generate random polygons for five random species over the landscape of Nigeria as follows:
s <- vect(system.file("ex/nigeria.json", package="phyloregion")) sp <- random_species(100, species=5, pol=s) pol <- polys2comm(dat = sp) head(pol[[1]][1:5, 1:5])
rast2comm
This third function, converts raster layers (often derived from species distribution modeling, such as aquamaps[@kaschner2008aquamaps]) to a community matrix.
fdir <- system.file("NGAplants", package="phyloregion") files <- file.path(fdir, dir(fdir)) ras <- rast2comm(files) head(ras[[1]][1:5, 1:5])
The object ras
above also returns two objects: a community data frame and a vector of grid cells with the numbers of species per cell and can be plotted as
a heatmap using plot
function as follows:
s <- vect(system.file("ex/SR_Naija.json", package="phyloregion")) par(mar=rep(0,4)) plot(s, "SR", border=NA, type = "continuous", col = hcl.colors(20, palette = "Blue-Red 3", rev=FALSE))
Community data are commonly stored in a matrix with the sites as rows and species / operational taxonomic units (OTUs) as columns. The elements of the matrix are numeric values indicating the abundance/observations or presence/absence (0/1) of OTUs in different sites. In practice, such a matrix can contain many zero values because species are known to generally have unimodal distributions along environmental gradients [@TerBraak2004], and storing and analyzing every single element of that matrix can be computationally challenging and expensive.
phyloregion
differs from other R packages (e.g. vegan [@vegan], picante [@Kembel2010]
or betapart[@Baselga2012]) in that the data are not stored in a (dense) matrix
or data.frame
but as a sparse matrix making use of the infrastructure provided by the Matrix package [@Matrix]. A sparse matrix is a matrix with a high proportion of zero entries[@Duff1977], of which only the non-zero entries are stored and used for downstream analysis.
A sparse matrix representation has two advantages. First the community matrix
can be stored in a much memory efficient manner, allowing analysis of larger
datasets. Second, for very large datasets spanning thousands of taxa and spatial scales,
computations with a sparse matrix are often much faster.
The phyloregion
package contains functions to conveniently change between data
formats.
library(Matrix) data(africa) sparse_comm <- africa$comm dense_comm <- as.matrix(sparse_comm) object.size(dense_comm) object.size(sparse_comm)
Here, the data set in the dense matrix representation consumes roughly five times more memory than the sparse representation.
We demonstrate the utility of phyloregion
in mapping standard conservation metrics of species richness, weighted endemism (weighted_endemism
) and threat (map_traits
) as well as fast computations of phylodiversity measures such as phylogenetic diversity (PD
), phylogenetic endemism (phylo_endemism
), and evolutionary distinctiveness and global endangerment (EDGE
). The major advantage of these functions compared to available tools is the ability to utilize sparse matrix that speeds up the analyses without exhausting computer memories, making it ideal for handling any data from small local scales to large regional and global scales.
weighted_endemism
Weighted endemism is species richness inversely weighted by species ranges[@crisp2001endemism],[@laffan2003assessing],[@daru2020endemism].
library(terra) data(africa) p <- vect(system.file("ex/sa.json", package = "phyloregion")) Endm <- weighted_endemism(africa$comm) m <- merge(p, data.frame(grids=names(Endm), WE=Endm), by="grids") m <- m[!is.na(m$WE),] par(mar=rep(0,4)) plot(m, "WE", col = hcl.colors(20, "Blue-Red 3"), type="continuous", border = NA)
PD
– phylogenetic diversityPhylogenetic diversity (PD
) represents the length of evolutionary pathways that connects a given set of taxa on a rooted phylogenetic tree [@Faith1992]. This metric is often characterised in units of time (millions of years, for dated phylogenies). We will map PD for plants of southern Africa.
data(africa) comm <- africa$comm tree <- africa$phylo poly <- vect(system.file("ex/sa.json", package = "phyloregion")) mypd <- PD(comm, tree) head(mypd) M <- merge(poly, data.frame(grids=names(mypd), pd=mypd), by="grids") M <- M[!is.na(M$pd),] head(M) par(mar=rep(0,4)) plot(M, "pd", border=NA, type="continuous", col = hcl.colors(20, "Blue-Red 3"))
phylo_endemism
– phylogenetic endemismPhylogenetic endemism is not influenced by variations in taxonomic opinion because it measures endemism based on the relatedness of species before weighting it by their range sizes[@Rosauer2009],[@daru2020endemism].
library(terra) data(africa) comm <- africa$comm tree <- africa$phylo poly <- vect(system.file("ex/sa.json", package = "phyloregion")) pe <- phylo_endemism(comm, tree) head(pe) mx <- merge(poly, data.frame(grids=names(pe), pe=pe), by="grids") mx <- mx[!is.na(mx$pe),] head(mx) par(mar=rep(0,4)) plot(mx, "pe", border=NA, type="continuous", col = hcl.colors(n=20, palette = "Blue-Red 3", rev=FALSE))
EDGE
– Evolutionary Distinctiveness and Global EndangermentThis function calculates EDGE by combining evolutionary distinctiveness (ED; i.e., phylogenetic isolation of a species) with global endangerment (GE) status as defined by the International Union for Conservation of Nature (IUCN).
data(africa) comm <- africa$comm threat <- africa$IUCN tree <- africa$phylo poly <- vect(system.file("ex/sa.json", package = "phyloregion")) x <- EDGE(threat, tree, Redlist = "IUCN", species="Species") head(x) y <- map_trait(comm, x, FUN = sd, pol=poly) par(mar=rep(0,4)) plot(y, "traits", border=NA, type="continuous", col = hcl.colors(n=20, palette = "Blue-Red 3", rev=FALSE))
The three commonly used methods for quantifying -diversity, the variation in species composition among sites, – Simpson, Sorenson and Jaccard[@laffan2016range]. The phyloregion
’s functions beta_diss
and phylobeta
compute efficiently pairwise dissimilarities matrices for large sparse community matrices and phylogenetic trees for taxonomic and phylogenetic turnover, respectively. The results are stored as distance objects for subsequent analyses.
phyloregion
offers a fast means of computing phylogenetic beta diversity, the turnover
of branch lengths among sites, making use of and improving on the infrastructure provided by the betapart
package[@Baselga2012] allowing a sparse community matrix as input.
data(africa) p <- vect(system.file("ex/sa.json", package = "phyloregion")) sparse_comm <- africa$comm tree <- africa$phylo tree <- keep.tip(tree, intersect(tree$tip.label, colnames(sparse_comm))) pb <- phylobeta(sparse_comm, tree)
y <- phyloregion(pb[[1]], pol=p)
plot_NMDS(y, cex=3) text_NMDS(y) par(mar=rep(0,4)) plot(y, palette="NMDS")
sessionInfo()
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