In sdray/adespatial: Multivariate Multiscale Spatial Analysis

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The package adespatial contains functions for the multiscale analysis of spatial multivariate data. It implements some new functions and reimplements existing functions that were available in packages of the sedaR project hosted on R-Forge (spacemakeR, packfor, AEM, etc.). It can be seen as a bridge between packages dealing with multivariate data (e.g., ade4, @Dray2007) and packages that deals with spatial data (sp, spdep). In adespatial, many methods consider the spatial information as a spatial weighting matrix (SWM), object of class listw provided by the spdep package (Figure 1). The SWM is defined as the Hadamard product (element-wise product) of a connectivity matrix by a weighting matrix. The binary connectivity matrix (spatial neighborhood, object of class nb) defines the pairs of connected and unconnected samples, while the weighting matrix allows weighting the connections, for instance to define that the strength of the connection between two samples decreases with the geographic distance.

Once SWM is defined, it can be used to build Moran's Eigenvector Maps (MEM, @Dray2006) that are orthogonal vectors maximizing the spatial autocorrelation (measured by Moran's coefficient). These spatial predictors can be used in multivariate statistical methods to provide spatially-explicit multiscale tools [@Dray2012]. This document provides a description of the main functionalities of the package.

Figure 1: Schematic representation of the functioning of the adespatial package. Classes are represented in pink frames and functions in blue frames. Classes and functions provided by adespatial are in bold.

To run the different analysis described, several packages are required and are loaded:

library(ade4)
library(adespatial)
library(adegraphics)
library(spdep)
library(sp)

The Mafragh data set

The Mafragh data set is used to illustrate several methods. It is available in the ade4 package and stored as a list:

data("mafragh")
class(mafragh)
names(mafragh)
dim(mafragh$flo)

The data.frame mafragh$flo is a floristic table that contains the abundance of 56 plant species in 97 sites in Algeria. Names of species are listed in mafragh$spenames. The geographic coordinates of the sites are given in mafragh$xy.

str(mafragh$env)

The data.frame mafragh$env contains 11 quantitative environmental variables. A map of the study area is also available (mafragh$Spatial.contour) that can be used as a background to display the sampling design:

mxy <- as.matrix(mafragh$xy)
rownames(mxy) <- NULL
s.label(mxy, ppoint.pch = 15, ppoint.col = "darkseagreen4", Sp = mafragh$Spatial.contour)

A more detailed description of the data set is available at http://pbil.univ-lyon1.fr/R/pdf/pps053.pdf (in French).

The functionalities of the adegraphics package [@Siberchicot2017] can be used to design simple thematic maps to represent data. For instance, it is possible to represent the spatial distribution of two species using the s.Spatial function applied on Voronoi polygons contained in mafragh$Spatial:

mafragh$spenames[c(1, 11), ]

fpalette <- colorRampPalette(c("white", "darkseagreen2", "darkseagreen3", "palegreen4"))
sp.flo <- SpatialPolygonsDataFrame(Sr = mafragh$Spatial, data = mafragh$flo, match.ID = FALSE)
s.Spatial(sp.flo[,c(1, 11)], col = fpalette(3), nclass = 3)

Building spatial neighborhood

Spatial neighborhoods are managed in spdep as objects of class nb. It corresponds to the notion of connectivity matrices discussed in @Dray2006 and can be represented by an unweighted graph. Various functions allow to create nb objects from geographic coordinates of sites. We present different alternatives according to the design of the sampling scheme.

Surface data

The function poly2nb allows to define neighborhood when the sampling sites are polygons and not points (two regions are neighbors if they share a common boundary). The resulting object can be plotted on a geographical map using the s.Spatial function of the adegraphics package [@Siberchicot2017].

data(mafragh)
class(mafragh$Spatial)
nb.maf <- poly2nb(mafragh$Spatial)
s.Spatial(mafragh$Spatial, nb = nb.maf, plabel.cex = 0, pnb.edge.col = 'red')

Regular grid and transect

If the sampling scheme is based on regular sampling (e.g., grid of 8 rows and 10 columns), spatial coordinates can be easily generated:

xygrid <- expand.grid(x = 1:10, y = 1:8)
s.label(xygrid, plabel.cex = 0)

For a regular grid, spatial neighborhood can be created with the function cell2nb. Two types of neighborhood can be defined. The queen specification considered horizontal, vertical and diagonal edges whereas the rook specification considered only horizontal and vertical edges:

nb2.q <- cell2nb(8, 10, type = "queen")
nb2.r <- cell2nb(8, 10, type = "rook")
s.label(xygrid, nb = nb2.q, plabel.cex = 0, main = "Queen neighborhood")
s.label(xygrid, nb = nb2.r, plabel.cex = 0, main = "Rook neighborhood")

The function cell2nb is the easiest way to deal with transects by considering a grid with only one row:

xytransect <- expand.grid(1:20, 1)
nb3 <- cell2nb(20, 1)

summary(nb3)

All sites have two neighbors except the first and the last one.

Irregular sampling

There are many ways to define the neighborhood in the case of irregular samplings. We consider a random subsample of 20 sites of the mafragh data set to better illustrate the differences between methods:

set.seed(3)
xyir <- mxy[sample(1:nrow(mafragh$xy), 20),]
s.label(xyir, main = "Irregular sampling with 20 sites")

The most intuitive way is to consider that sites are neighbors (or not) according to the distances between them. This definition is provided by the dnearneigh function:

nbnear1 <- dnearneigh(xyir, 0, 50)
nbnear2 <- dnearneigh(xyir, 0, 305)

g1 <- s.label(xyir, nb = nbnear1, pnb.edge.col = "red", main = "neighbors if 0<d<50", plot = FALSE)
g2 <- s.label(xyir, nb = nbnear2, pnb.edge.col = "red", main = "neighbors if 0<d<305", plot = FALSE)
cbindADEg(g1, g2, plot = TRUE)

Using a distance-based criteria could lead to unbalanced graphs. For instance, if the maximum distance is too low, some points have no neighbors:

nbnear1

On the other hand, if the maximum distance is too high, all sites are connected:

nbnear2

It is also possible to define neighborhood by a criteria based on nearest neighbors. However, this option can lead to non-symmetric neighborhood: if site A is the nearest neighbor of site B, it does not mean that site B is the nearest neighbor of site A.

The function knearneigh creates an object of class knn. It can be transformed into a nb object with the function knn2nb. This function has an argument sym which can be set to TRUE to force the output neighborhood to symmetry.

knn1 <- knearneigh(xyir, k = 1)
nbknn1 <- knn2nb(knn1, sym = TRUE)
knn2 <- knearneigh(xyir, k = 2)
nbknn2 <- knn2nb(knn2, sym = TRUE)

g1 <- s.label(xyir, nb = nbknn1, pnb.edge.col = "red", main = "Nearest neighbors (k=1)", plot = FALSE)
g2 <- s.label(xyir, nb = nbknn2, pnb.edge.col = "red", main = "Nearest neighbors (k=2)", plot = FALSE)
cbindADEg(g1, g2, plot = TRUE)

This definition of neighborhood can lead to unconnected subgraphs. The function n.comp.nb finds the number of disjoint connected subgraphs:

n.comp.nb(nbknn1)

More elaborate procedures are available to define neighborhood. For instance, Delaunay triangulation is obtained with the function tri2nb. It requires the package deldir. Other graph-based procedures are also available:

nbtri <- tri2nb(xyir)
nbgab <- graph2nb(gabrielneigh(xyir), sym = TRUE)
nbrel <- graph2nb(relativeneigh(xyir), sym = TRUE)

g1 <- s.label(xyir, nb = nbtri, pnb.edge.col = "red", main = "Delaunay", plot = FALSE)
g2 <- s.label(xyir, nb = nbgab, pnb.edge.col = "red", main = "Gabriel", plot = FALSE)
g3 <- s.label(xyir, nb = nbrel, pnb.edge.col = "red", main = "Relative", plot = FALSE)

ADEgS(list(g1, g2, g3))    

The adespatial functions chooseCN and listw.candidates provides simple ways to build spatial neighborhoods. They are wrappers of many of the spdep functions presented above. The function listw.explore is an interactive graphical interface that allows to generate R code to build neighborhood objects (see Figure 2).

Manipulating nb objects

A nb object is not stored as a matrix. It is a list of neighbors. The neighbors of the first site are in the first element of the list:

nbgab[[1]]

Various tools are provided by spdep to deal with these objects. For instance, it is possible to identify differences between two neighborhoods:

diffnb(nbgab, nbrel)

Usually, it can be useful to remove some connections due to edge effects. In this case, the function edit.nb provides an interactive tool to add or delete connections.

The function include.self allows to include a site in its own list of neighbors (self-loops). The spdep package provides many other tools to manipulate nb objects:

intersect.nb(nb.obj1, nb.obj2)
union.nb(nb.obj1, nb.obj2)
setdiff.nb(nb.obj1, nb.obj2)
complement.nb(nb.obj)
droplinks(nb, drop, sym = TRUE)
nblag(neighbours, maxlag)

Defining spatial weighting matrices {#swm}

A spatial weighting matrices (SWM) is computed by a transformation of a spatial neighborhood. We consider the Gabriel graph for the full data set:

nbgab <- graph2nb(gabrielneigh(mxy), sym = TRUE)

In R, SWM are not stored as matrices but as objects of the class listw. This format is more efficient than a matrix representation to manage large data sets. An object of class listw can be easily created from an object of class nb with the function nb2listw.

Different objects listw can be obtained from a nb object. The argument style allows to define a transformation of the matrix such as standardization by row sum, by total sum or binary coding, etc. General spatial weights can be introduced by the argument glist. This allows to introduce, for instance, a weighting relative to the distances between the points. For this task, the function nbdists is very useful as it computes Euclidean distance between neighbor sites defined by an nb object.

To obtain a simple row-standardization, the function is simply called by:

nb2listw(nbgab)

More sophisticated forms of spatial weighting matrices can be defined. For instance, it is possible to weight edges between neighbors as functions of geographic distances. In a fist step, distances between neighbors are obtained by the function \texttt{nbdists}:

distgab <- nbdists(nbgab, mxy)
nbgab[[1]]
distgab[[1]]

Then, spatial weights are defined as a function of distance (e.g. $1-d_{ij}/max(d_{ij})$):

fdist <- lapply(distgab, function(x) 1 - x/max(dist(mxy)))

And the spatial weighting matrix is then created:

listwgab <- nb2listw(nbgab, glist = fdist)
listwgab
names(listwgab)
listwgab$neighbours[[1]]
listwgab$weights[[1]]

The matrix representation of a listw object can also be obtained:

print(listw2mat(listwgab)[1:10, 1:10], digits = 3)

To facilitate the building of spatial neighborhoods (nb object) and associated spatial weighting matrices (listw object), the package adespatial provides several tools. An interactive graphical interface is launched by the call listw.explore() assuming that spatial coordinates are still stored in an object of the R session (Figure 2).

Figure 2: The interactive interface provided by the function listw.explore.

Creating spatial predictors

The package adespatial provide different tools to build spatial predictors that can be incorporated in multivariate analysis. They are orthogonal vectors stored in a object of class orthobasisSp. Orthogonal polynomials of geographic coordinates can be computed by the function orthobasis.poly whereas principal coordinates of neighbour matrices (PCNM, @Borcard2002) are obtained by the function dbmem.

The Moran's Eigenvectors Maps (MEMs) provide the most flexible framework. If we consider the $n \times n$ spatial weighting matrix $\mathbf{W} = [w_{ij}]$, they are the $n-1$ eigenvectors obtained by the diagonalization of the doubly-centred SWM:

$$ \mathbf{\Omega V}= \mathbf{V \Lambda} $$

where $\mathbf{\Omega} = \mathbf{HWH}$ is the doubly-centred SWM and $\mathbf{H} = \left ( \mathbf{I}-\mathbf{11}\tr /n \right )$ is the centring operator.

MEMs are orthogonal vectors with a unit norm that maximize Moran's coefficient of spatial autocorrelation [@Griffith1996; @Dray2012] and are stored in matrix $\mathbf{V}$.

MEMs are provided by the functions scores.listw or mem of the adespatial package. These two functions are exactly identical (both are kept for historical reasons and compatibility) and return an object of class orthobasisSp.

mem.gab <- mem(listwgab)
mem.gab

This object contains MEMs, stored as a data.frame and other attributes:

class(mem.gab)
names(attributes(mem.gab))

The eigenvalues associated to MEMs are stored in the attribute called values:

oldpar <- par(mar = c(0, 2, 3, 0))
    barplot(attr(mem.gab, "values"), 
        main = "Eigenvalues of the spatial weighting matrix", cex.main = 0.7)
par(oldpar)

A plot method is provided to represent MEMs. By default, eigenvectors are represented as a table (sites as rows, MEMs as columns). This representation is usually not informative and it is better to map MEMs in the geographical space by documenting the argument SpORcoords:

plot(mem.gab[,c(1, 5, 10, 20, 30, 40, 50, 60, 70)], SpORcoords = mxy)

or using the more flexible s.value function:

s.value(mxy, mem.gab[,c(1, 5, 10, 20, 30, 40, 50, 60, 70)], symbol = "circle", ppoint.cex = 0.6)

Moran's I can be computed and tested for each eigenvector with the moran.randtest function:

moranI <- moran.randtest(mem.gab, listwgab, 99)

As demonstrated in @Dray2006, eigenvalues and Moran's I are equal (post-multiply by a constant):

head(attr(mem.gab, "values") / moranI$obs)

Describing spatial patterns

In the previous sections, we considered only the spatial information as a geographic map, a spatial weighting matrix (SWM) or a basis of spatial predictors (e.g., MEM). In the next sections, we will show how the spatial information can be integrated to analyze multivariate data and identify multiscale spatial patterns. The dataset mafragh available in ade4 will be used to illustrate the different methods.

Moran's coefficient of spatial autocorrelation {#mc}

The SWM can be used to compute the level of spatial autocorrelation of a quantitative variable using the Moran's coefficient. If we consider the $n \times 1$ vector $\mathbf{x} = \left ( {x_1 \cdots x_n } \right )\tr$ containing measurements of a quantitative variable for $n$ sites and $\mathbf{W} = [w_{ij}]$ the SWM. The usual formulation for Moran's coefficient (MC) of spatial autocorrelation is: $$ MC(\mathbf{x}) = \frac{n\sum\nolimits_{\left( 2 \right)} {w_{ij} (x_i -\bar {x})(x_j -\bar {x})} }{\sum\nolimits_{\left( 2 \right)} {w_{ij} } \sum\nolimits_{i = 1}^n {(x_i -\bar {x})^2} }\mbox{ where }\sum\nolimits_{\left( 2 \right)} =\sum\limits_{i = 1}^n {\sum\limits_{j = 1}^n } \mbox{ with }i\ne j $$

MC can be rewritten using matrix notation: $$ MC(\mathbf{x}) = \frac{n}{\mathbf{1}\tr\mathbf{W1}}\frac{\mathbf{z}\tr{\mathbf{Wz}}}{\mathbf{z}\tr\mathbf{z}} $$ where $\mathbf{z} = \left ( \mathbf{I}-\mathbf{1}\mathbf{1}\tr /n \right )\mathbf{x}$ is the vector of centred values (i.e., $z_i = x_i-\bar{x}$).

The function moran.mc of the spdep package allows to compute and test, by permutation, the significance of the Moran's coefficient. A wrapper is provided by the moran.randtest function to test simultaneously and independently the spatial structure for several variables.

sp.env <- SpatialPolygonsDataFrame(Sr = mafragh$Spatial, data = mafragh$env, match.ID = FALSE)
maps.env <- s.Spatial(sp.env, col = fpalette(6), nclass = 6)
MC.env <- moran.randtest(mafragh$env, listwgab, nrepet = 999)
MC.env

For a given SWM, the upper and lower bounds of MC \citep{Jong1984} are equal to $\lambda_{max} (n/\mathbf{1}\tr\mathbf{W1})$ and $\lambda_{min} (n/\mathbf{1}\tr\mathbf{W1})$ where $\lambda_{max}$ and $\lambda_{min}$ are the extreme eigenvalues of $\mathbf{\Omega}$. These extreme values are returned by the moran.bounds function:

mc.bounds <- moran.bounds(listwgab)
mc.bounds

Hence, it is possible to display Moran's coefficients computed on environmental variables and the minimum and maximum values for the given SWM:

env.maps <- s1d.barchart(MC.env$obs, labels = MC.env$names, plot = FALSE, xlim = 1.1 * mc.bounds, paxes.draw = TRUE, pgrid.draw = FALSE)
addline(env.maps, v = mc.bounds, plot = TRUE, pline.col = 'red', pline.lty = 3)

Decomposing Moran's coefficient

The standard test based on MC is not able to detect the coexistence of positive and negative autocorrelation structures (i.e., it leads to a non-significant test). The moranNP.randtest function allows to decompose the standard MC statistic into two additive parts and thus to test for positive and negative autocorrelation separately [@Dray2011]. For instance, we can test the spatial distribution of Magnesium. Only positive autocorrelation is detected:

NP.Mg <- moranNP.randtest(mafragh$env[,5], listwgab, nrepet = 999, alter = "two-sided") 
NP.Mg
plot(NP.Mg)
sum(NP.Mg$obs)
MC.env$obs[5]

MULTISPATI analysis

When multivariate data are considered, it is possible to search for spatial structures by computing univariate statistics (e.g., Moran's Coefficient) on each variable separately. Another alternative is to summarize data by multivariate methods and then detect spatial structures using the output of the analysis. For instance, we applied a centred principal component analysis on the abundance data:

pca.hell <- dudi.pca(mafragh$flo, scale = FALSE, scannf = FALSE, nf = 2)

MC can be computed for PCA scores and the associated spatial structures can be visualized on a map:

moran.randtest(pca.hell$li, listw = listwgab)
s.value(mxy, pca.hell$li, Sp = mafragh$Spatial.contour, symbol = "circle", col = c("white", "palegreen4"), ppoint.cex = 0.6)

PCA results are highly spatially structured. Results can be optimized, compared to this two-step procedure, by searching directly for multivariate spatial structures. The multispati function implements a method [@Dray2008] that search for axes maximizing the product of variance (multivariate aspect) by MC (spatial aspect):

ms.hell <- multispati(pca.hell, listw = listwgab, scannf = F)

The summary method can be applied on the resulting object to compare the results of initial analysis (axis 1 (RS1) and axis 2 (RS2)) and those of the multispati method (CS1 and CS2):

summary(ms.hell)

The MULTISPATI analysis allows to better identify spatial structures (higher MC values).

Scores of the analysis can be mapped and highlight some spatial patterns of community composition:

g.ms.maps <- s.value(mafragh$xy, ms.hell$li, Sp = mafragh$Spatial.contour, symbol = "circle", col = c("white", "palegreen4"), ppoint.cex = 0.6)

The spatial distribution of several species can be inserted to facilitate the interpretation of the outputs of the analysis:

g.ms.spe <- s.arrow(ms.hell$c1, plot = FALSE)
g.abund <- s.value(mxy, mafragh$flo[, c(12,11,31,16)],
    Sp = mafragh$Spatial.contour, symbol = "circle", col = c("black", "palegreen4"), plegend.drawKey = FALSE, ppoint.cex = 0.4, plot = FALSE)
p1 <- list(c(0.05, 0.65), c(0.01, 0.25), c(0.74, 0.58), c(0.55, 0.05))
for (i in 1:4)
g.ms.spe <- insert(g.abund[[i]], g.ms.spe, posi = p1[[i]], ratio = 0.25, plot = FALSE)
g.ms.spe

Multiscale analysis with MEM

All the methods presented in the previous section consider the whole SWM to integrate the spatial information. In this section, we present alternatives that use MEM to introduce the notion of space at multiple scales.

Scalogram and MSPA

The full set of MEMs provide a basis of orthogonal vectors that can be used to decompose the total variance of a given variable at multiple scales. This approach consists simply in computing $R^2$ values associated to each MEM to build a scalogram indicating the part of variance explained by each MEM. These values can be tested by a permutation procedure. Here, we illustrate the procedure with the abundance of Bolboschoenus maritimus (Sp11) which is mainly located in the central part of the study area:

scalo <- scalogram(mafragh$flo[,11], mem.gab)
plot(scalo)

As the number of MEMs is equal to the number of sites minus one and as MEMs are othogonal, the variance is fully decomposed:

sum(scalo$obs)

When the number of MEMs is high, the results provided by this approach can be difficult to interpret. In this case it can be advantageous to use smoothed scalograms (using the nblocks argument) where spatial components are formed by groups of successive MEMs:

plot(scalogram(mafragh$flo[,11], mem(listwgab), nblocks = 20))

It is possible to compute scalograms for all the species of the data table. These scalograms can be stored in a table and analysing this table with a PCA allows to identify the important scales of the data set and the similarities between species based on their spatial distributions [@Jombart2009]. This analysis named Multiscale Patterns Analysis (MSPA) is available in the mspa function that takes the results of a multivariate analysis (an object of class dudi) as argument:

mspa.hell <- mspa(pca.hell, listwgab, scannf = FALSE, nf = 2)

g.mspa <- scatter(mspa.hell, posieig = "topright", plot = FALSE)
g.mem <- s.value(mafragh$xy, mem.gab[, c(1, 2, 6, 3)], Sp = mafragh$Spatial.contour, ppoints.cex = 0.4, plegend.drawKey = FALSE, plot = FALSE)
g.abund <- s.value(mafragh$xy, mafragh$flo[, c(31,54,25)], Sp = mafragh$Spatial.contour, symbol = "circle", col = c("black", "palegreen4"), plegend.drawKey = FALSE, ppoint.cex = 0.4, plot = FALSE)

p1 <- list(c(0.01, 0.44), c(0.64, 0.15), c(0.35, 0.01), c(0.15, 0.78))
for (i in 1:4)
g.mspa <- insert(g.mem[[i]], g.mspa, posi = p1[[i]], plot = FALSE)

p2 <- list(c(0.27, 0.54), c(0.35, 0.35), c(0.75, 0.31))
for (i in 1:3)
g.mspa <- insert(g.abund[[i]], g.mspa, posi = p2[[i]], plot = FALSE)

g.mspa

Selection of SWM and MEM

Scalograms and MSPA require the full set of MEMs to decompose the total variation. However, regression-based methods (described in next sections) could suffer from overfitting if the number of explanatory variables is too high and thus require a procedure to reduce the number of MEMs. The function mem.select proposes different alternatives to perform this selection using the argument method [@Bauman2018]. By default, only MEMs associated to positive eigenvalues are considered (argument MEM.autocor = "positive") and a forward selection (based on $R^2$ statistic) is performed after a global test (method = "FWD"):

mem.gab.sel <- mem.select(pca.hell$tab, listw = listwgab)
mem.gab.sel$global.test
mem.gab.sel$summary

Results of the global test and of the forward selection are returned in elements global.test and summary. The subset of selected MEMs are in MEM.select and can be used in subsequent analysis (see sections on Redundancy Analysis and Variation Partitioning).

class(mem.gab.sel$MEM.select)
dim(mem.gab.sel$MEM.select)

Different SWMs can be defined for a given data set. An important issue concerns the selection of a SWM. This choice can be driven by biological hypotheses but a data-driven procedure is provided by the listw.select function. A list of potential candidates can be built using the listw.candidates function. Here, we create four candidates using two definitions for neighborhood (Gabriel and Relative graphs using c("gab", "rel")) and two weighting functions (binary and linear using c("bin", "flin")):

cand.lw <- listw.candidates(mxy, nb = c("gab", "rel"), weights = c("bin", "flin"))

The function listw.select proposes different methods for selecting a SWM [@Bauman2018a]. The procedure is very similar to the one proposed by mem.select except that p-value corrections are applied on global tests taking into account the fact that several candidates are used. By default (method = "FWD"), it applies forward selection on the significant SWMs and selects among these the SWM for which the subset of MEMs yields the highest adjusted R.

sel.lw <- listw.select(pca.hell$tab, candidates = cand.lw, nperm = 99)

A summary of the procedure is available:

sel.lw$candidates
sel.lw$best.id

The corresponding SWM can be obtained by

lw.best <- cand.lw[[sel.lw$best.id]]

The subset of MEMs corresponding to the best SWM is also returned by the function:

sel.lw$best

Canonical Analysis {#rda}

Canonical methods are widely used to explain the structure of an abundance table by environmental and/or spatial variables. For instance, Redundancy Analysis (RDA) is available in functions pcaiv (package ade4) or rda (package vegan). RDA can be applied using selected MEMs as explanatory variables to study the spatial patterns in plant communities, :

rda.hell <- pcaiv(pca.hell, sel.lw$best$MEM.select, scannf = FALSE)

The permutation test based on the percentage of variation explained by the spatial predictors ($R^2$) is highly significant:

test.rda <- randtest(rda.hell)
test.rda
plot(test.rda)

Associated spatial structures can be mapped:

s.value(mxy, rda.hell$li, Sp = mafragh$Spatial.contour, symbol = "circle", col = c("white", "palegreen4"), ppoint.cex = 0.6)

Variation partitioning {#varpart}

Spatial structures identified by Redundancy Analysis in the previous section can be due to niche filtering or other processes (e.g., neutral dynamics). Variation partitioning [@Borcard1992] based on adjusted $R^2$ [@Peres-Neto2006a] can be used to identify the part of spatial structures that can be explained or not by environmental predictors. This method is implemented in the function varpart of package vegan that is able to deal with up to four tables of predictors:

library(vegan)
vp1 <- varpart(pca.hell$tab, mafragh$env, sel.lw$best$MEM.select)
vp1
plot(vp1, bg = c(3, 5), Xnames = c("environment", "spatial"))

A simpler function varipart is available in ade4 that is able to deal only with two tables of explanatory variables:

vp2 <- varipart(pca.hell$tab, mafragh$env, sel.lw$best$MEM.select)
vp2

Estimates and testing procedures associated to standard variation partitioning can be biased in the presence of spatial autocorrelation in both response and explanatory variables. To solve this issue, adespatial provides functions to perform spatially-constrained randomization using Moran's Spectral Randomization.

Testing with Moran's Spectral Randomization {#msr}

Moran's Spectral Randomization (MSR) allows to generate random replicates that preserve the spatial structure of the original data [@Wagner2015]. These replicates can be used to create spatially-constrained null distribution. For instance, we consider the case of bivariate correlation between Elevation and Sodium:

cor(mafragh$env[,10], mafragh$env[,11])

This correlation can be tested by a standard t-test:

cor.test(mafragh$env[,10], mafragh$env[,11])

However this test assumes independence between observations. This condition is not observed in our data as suggested by the computation of MC:

moran.randtest(mafragh$env[,10], lw.best)

An alternative is to generate random replicates for the two variables with same level of spatial autocorrelation:

msr1 <- msr(mafragh$env[,10], lw.best)
summary(moran.randtest(msr1, lw.best, nrepet = 2)$obs)

msr2 <- msr(mafragh$env[,11], lw.best)

Then, the statistic is computed on observed and simulated data to build a randomization test:

obs <- cor(mafragh$env[,10], mafragh$env[,11])
sim <- sapply(1:ncol(msr1), function(i) cor(msr1[,i], msr2[,i]))
testmsr <- as.randtest(obs = obs, sim = sim, alter = "two-sided")
testmsr

The function msr is generic and several methods are implemented in adespatial. For instance, it can be used to correct estimates and significance of the environmental fraction in the case of a variation partitioning [@Clappe2018] computed with the varipart function:

msr(vp2, listwORorthobasis = lw.best)

References

sdray/adespatial documentation built on March 30, 2024, 12:30 a.m.