Supporting Information Environmental harshness is positively correlated with intraspecific divergence in mammals and birds Carlos A. Botero, Roi Dor, Christy M. McCain, and Rebecca J. Safran Contents - Data S1 Spatial sensitivity analysis - Data S2 Sample code for Bayesian Phylogenetic Mixed Models (BPMM) in R - Figure S1 Elevation gradients of the world and three representative examples of species whose breeding ranges are dissected by mountains - Table S1 Principal components analyses of continuous bio-ecological variables in the spatial sensitivity analysis - Table S2 Summary of results for the Bayesian Phylogenetic Mixed Models of subspecies richness in the spatial sensitivity analysis - Table S3 Summary of results for the Bayesian Phylogenetic Mixed Models of subspecies richness in north temperate mammals and birds Data S1. Spatial sensitivity analysis To explore the extent to which our results are influenced by spatial variation in environmental conditions, we replicated our analyses 100 times using datasets in which environmental variables were extracted from randomly chosen localities within each species’ range (rather than averaged across the entire breeding range). Table S1 summarizes the results of a PCA combining these 100 datasets for birds and 100 datasets for mammals. The resulting principal components are nearly identical to those derived from the analysis of environmental means (see Table 1 in the main text), including a similarly decreasing amount of variance explained by ‘Environmental Harshness’ (PC1), Geographic Coverage (PC2), Precipitation unpredictability (PC3), and Residual Body Size (PC4). The combined results of BPMMs on these 100 datasets per group (Table S2) indicate that the effects described in Table 3 of the main text are quite robust to spatial variation in environmental variables. With the exception of rainfall unpredictability and body size in mammals, the estimated effects of the remaining putative predictors are consistent with our earlier findings in both magnitude and significance. In particular, the mean coefficients estimated for environmental harshness and geographic coverage are nearly identical to those presented in the main text. Data S2. Example code for Bayesian Phylogenetic Mixed Models (BPMM) in R The following is an example of the general stipulation of our MCMCglmm models: # fully parameterized model require (MCMCglmm) Ainv<-inverseA(mytree)$Ainv prior = list( B = list(mu = rep(0,14), V = diag(14)), R = list(V = diag(1), nu = 0.002), G = list( G1 = list(V = diag(1), n = 0.002 ) ) ) fullmod <- MCMCglmm( (subspecies - 1) ~ 1 + DissectedByMountains + EnvShielding + Glaciation + IslandDwelling + LogAge + LogEnvHarshness + Area + RainfallUnpred + I(RainfallUnpred^2) + BS + LogEnvHarshness*DissectedByMountains + LogEnvHarshness* EnvShielding + RainfallUnpred* EnvShielding, data = mydata, random=~Species, ginverse=list(Species=Ainv), family = "poisson", prior= prior, nitt = 300000, burnin = 10000, thin = 50) # evaluate convergence geweke.diag(fullmod$Sol) # Geweke (1992) diagnostic test heidel.diag(fullmod$Sol) # Heidelberg and Welch (1983) diagnostic test plot(fullmod$Sol) # visual inspection of mixing properties of the MCMC chain # now explore results... summary(fullmod) Figure S1. Elevation gradients of the world (dark green) as defined by slopes equal or higher than 5 degrees (criterion based on UN Mountain Watch category 5, UNEP World Conservation Monitoring Centre 2002). The bottom panels depict representative examples of species whose breeding ranges (red areas) are divided into two or more geographically isolated sections by the intersection of mountain chains: Apodemus sylvaticus (A); Bradypus variegatus (B); Aonyx cinerea (C). Table S1. Principal components analyses of continuous bio-ecological variables in the spatial sensitivity analysis. Data from 100 randomly selected locations within the breeding range of each mammal and bird species in the main model are included. Standardized loadings of the main contributors to each component are highlighted in boldface. Environmental harshness (PC1) Geographic coverage (PC2) Precipitation unpredictability (PC3) Residual body size (PC4) Uniqueness 0.90 0.01 0.13 0.03 0.18 Predictability of temperature cycles -0.87 0.01 -0.15 0.02 0.22 sqrt (mean precipitation) -0.86 0.10 0.15 -0.05 0.22 (Mean temperature)2 -0.75 0.20 0.05 0.01 0.40 Net primary productivity -0.69 0.20 0.07 -0.21 0.43 -0.71 0.16 0.44 0.01 0.28 0.61 0.36 0.24 -0.33 0.34 0.29 0.81 -0.03 -0.32 0.17 0.09 0.57 -0.21 0.77 0.03 -0.18 0.06 -0.87 -0.29 0.13 4.33 1.22 1.12 0.93 0.43 0.55 0.67 0.76 Bio-ecological variable ln (Annual variance in temperature) sqrt (Annual variance in precipitation) Habitat heterogeneity ln (Area) ln (Body size) Predictability of precipitation cycles SS loadings % Cumulative variance explained Table S2. Summary of results for Bayesian Phylogenetic Mixed Models of subspecies richness in the spatial sensitivity analysis. Estimates of posterior means reflect in this case the average parameters estimated from 100 datasets using random localities for every species. Mammals † Birds † Parameter Posterior mean (95% CI) f‡ Posterior mean (95% CI) f‡ Intercept -1.92 (-3.33, -0.52)** 1.00 -2.32 (-2.96, -1.68)*** 1.00 0.87 (0.70, 1.05)*** 1.00 0.42 (0.34, 0.50)*** 1.00 Environmental shielding § N.S. 0.00 N.S. 0.00 Glaciation N.S. 0.00 N.S. 0.00 Island dwelling 0.57 (0.31, 0.84)*** 1.00 0.62 (0.51, 0.73)*** 1.00 ln( species age ) N.S. 0.00 N.S. 0.00 ln( environmental harshness, PC1 ) 1.17 (0.87, 1.47)*** 1.00 0.79 (0.59, 0.98)*** 1.00 Geographic coverage, PC2 0.85 (0.72, 0.99)*** 1.00 0.69 (0.61, 0.77)*** 1.00 Precipitation unpredictability, PC3 N.S. 0.03 0.05 (0.01, 0.09)* 0.82 PC32 N.S. 0.30 N.S. 0.09 Residual body size, PC4 N.S. 0.00 -0.35 (-0.43, -0.27)*** 1.00 ln( environmental harshness) * Environmental shielding N.S. 0.00 N.S. 0.20 Precipitation unpredictability * Environmental shielding N.S. 0.00 N.S. 0.00 Dissected by mountains † N.S. = not-significant; p MCMC = 0.05; * p MCMC < 0.05; ** p MCMC < 0.01; *** p MCMC < 0.001 ‡ f = frequency of spatial datasets in which MCMC p-values < 0.05 § Hibernation in mammals, migration in birds Table S3. Summary of results for the Bayesian Phylogenetic Mixed Models of subspecies richness in north temperate mammals and birds † Mammals ‡ Birds ‡ Parameter Posterior mean (95% CI) Posterior mean (95% CI) f§ Intercept -0.90 (-2.03, 0.22) -0.41 (-1.07, 0.24) 0.00 Glaciation N.S. N.S. 0.00 Island dwelling N.S. N.S. 0.00 ln( species age ) N.S. N.S. 0.00 0.46 (0.09, 0.87)* 0.53 (0.16, 0.90)* 1.00 0.96 (0.71, 1.22)*** 0.60 (0.26, 0.94)*** 1.00 N.S. N.S. 0.00 -0.28 (-0.52, -0.03)* -0.35 (-0.59, -0.12)* 1.00 Environmental harshness, PC1 Geographic coverage, PC2 Precipitation unpredictability, PC3 Residual body size, PC4 † Only non-migratory species whose ranges are entirely above 23.4°N latitude were considered for these analyses ‡ N.S. = not-significant; p MCMC = 0.05; * p MCMC < 0.05; < 0.001; § f = frequency of trees for which MCMC p-values < 0.05 ** p MCMC < 0.01; *** p MCMC Supporting References UNEP World Conservation Monitoring Centre (2002). UNEP World Conservation Monitoring Centre: Mountain Watch. Cambridge, UK.