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Published in final edited form as: Curr Biol. 2017 Apr 27;27(9):1369–1374. doi: 10.1016/j.cub.2017.03.046

The geography of ecological niche evolution in mammals

Florent Mazel 1, Rafael O Wüest 2,3, Maya Gueguen 4, Julien Renaud 5, Gentile Francesco Ficetola 6,7, Sébastien Lavergne 8, Wilfried Thuiller 9
PMCID: PMC5489078  EMSID: EMS73202  PMID: 28457870

Summary

Convergent adaptive evolution of species’ ecological niches — i.e. the appearance of similar niches in independent lineages—is the result of natural selection acting on niche-related species traits (‘traits’ hereafter) and contrasts with neutral evolution [14]. While trait convergences are recognized as being of importance at the species scale, we still know little about the impact of species convergence on the overall trait and niche structure of entire biotas at large spatial scales [5]. Here, we map the convergent evolution of four traits (diet, body-mass, activity cycle and foraging strata) for mammal species and assemblages (defined at 200x200km resolution) at a global scale. Using data on the geographic distributions, traits, and phylogenetic relationships of species and by comparing observed patterns of trait β-diversity to evolutionary neutral expectations, we show that trait convergence is not restricted to particular lineages, but scales up to entire assemblages (i.e. whole species communities). We find region-wide biota convergence in traits between regions with similar climates, particularly between Australia and other continents. Pairs of assemblages that show trait divergence often involve arctic regions where rapid evolutionary changes occurred in response to extreme climatic constraints. By integrating both macro-ecological and macro-evolutionary approaches into a single framework, our study quantifies the crucial role of evolutionary processes such as natural selection in the spatial distribution and structure of large-scale species assemblages.

Keywords: Community convergence, Community divergence, Marsupials, trait beta-diversity, functional beta-diversity, neutral evolution, Brownian motion

Results and Discussion

Convergent evolution caused by natural selection occurs when independent lineages that experience the same environmental constraints evolve similar morphological, physiological and/or behavioural traits [1,4], ultimately leading them to occupy similar ecological niches. Parallelism, where similar trait changes occur in closely-related ancestors, is sometimes distinguished from convergence because it usually occurs at a smaller phylogenetic scale. However, parallelism and convergence are part of a continuum, hampering any clear distinction among them [1,4], thus, we use the term convergence for all phylogenetic scales (as proposed by ref [4], ‘parallelism’ should be restricted to characterize the degree of molecular similarities underlying phenotypic convergences). Convergent evolution leads to higher ecological niche and trait similarity between unrelated species than expected under neutral evolution, where niches or traits shift along a continuous axis or between discrete states in a random way through evolutionary time [2,3,6,7]. While these neutral-like evolution can be generated by randomly fluctuating natural selection [8] typical random walk models still represent the most realistic macroevolutionary models of neutral evolution so far. There is empirical evidence of convergent trait and niche evolution in all major kingdoms [3,912] but this has not yet been quantified at the species scale for large clades, or at the scale of entire species assemblages at broad spatial scales (e.g. grid-based assemblages).

Here, we report the first global analysis of species-level evolutionary convergence and divergence of ecological niches for 4,736 terrestrial mammals. Species ecological niches were defined using a set of four traits (diet, body-mass, activity cycle and foraging strata) that produce a coarse representation of animal Eltonian niches [1316]. While diet and body mass directly refer to species resource requirement, foraging location and activity represent behavioural traits reflecting how species acquire food from their environment. We developed a phylogenetically standardized trait distance metric that contrasts observed trait distances between species pairs (i.e. all possible pairs of species in the dataset – not only sister-species pairs) to trait distances expected under a neutral (Brownian or Markov) model of trait evolution with a single rate [3,6,17] [metric = (observed distance – mean expected distances) / standard deviation of expected distances, see Supplemental Experimental Procedures and Table S1-S2]. Observed and neutral distances were computed using the Gower distance metric, which allows mixing categorical and continuous traits. Negative (positive) standardized trait distances mean that observed distances are lower (higher) than neutral expectations, suggesting trait convergences (divergences) between species.

Overall, extreme niche convergence and divergence between species pairs, as assessed by the four traits, were widespread across the mammalian Tree of life (Figure 1 and S1). Pairs of species harbouring higher trait similarities than expected under neutral evolution included the classical examples of marsupial-placental convergence. For example, Artiodactyla (e.g. deer) and Diprotodontia (e.g. kangaroo), as well as Soricomorpha (e.g. shrews) and some Dasyuromorphia species (“shrew-like marsupials”) show low phylogenetically standardized functional trait distances, because they both involved clades which evolved toward large herbivore phenotypes and small insectivore phenotypes, respectively. Within the placentals, “shrew-like species” from different orders like Afrosoricida (e.g. shrew tenrecs) and Soricomorpha also showed higher functional trait convergence than expected under a neutral model of evolution. In these cases, convergence has been so strong that even former morphology-based systematics mistakenly grouped these species into the same paraphyletic order [18] (Insectivora). These convergences probably result from strong energetic constraints related to a strictly insectivorous diet in specific climatic conditions: insectivores preying on small insects are generally very small (are at the lower body size limit for a mammal physiology) and have very similar teeth morphology [19] . Variations in morphological traits, especially body mass, have also commonly be related to climatic gradient (referred to as Bergmann's rule), thereby generating similar body mass patterns in independent species assemblages occupying equivalent climatic space. Bats also showed low levels of functional trait distance within their own order (Figure 1), because a large number of bats share the same diet, and therefore harbour trait conservatism (i.e. the tendency for lineages to retain ancestral traits [20,21]). Closely related species can have very divergent traits, especially within Dasyuromorphia (marsupial Carnivores) or Carnivora (Figure 1). Divergent pairs of species (i.e. species harbouring divergent traits) within Carnivora generally inhabit very distinct environments, for instance with one living in a temperate or tropical region, and another inhabiting arctic regions (e.g. polar bear vs. other bears [22]), which suggests an interplay between high dispersal capabilities followed by strong natural selection, especially for top predators in the Arctic.

Figure 1. Patterns of species convergence and divergence across and within the main orders of mammals.

Figure 1

The figure shows a network representation of convergence (A) and divergence (B) patterns at the species scale. Nodes represent the main mammalian orders involved in either the top 0.1% of convergent (A) or top 0.1% of divergent pairs of species (B). Edges between nodes depict convergence/divergence events between (or within, when a node is linked to itself) orders. Edge width indicates the relative number of pairs of species involved in convergence/divergence events, standardized by the relative richness of each order (edge length is arbitrary). See also Figure S1.

While trait convergence and divergence patterns at the species scale seem to be present in mammals, it remains unknown whether and how these species scale patterns contribute to the trait structure of entire species assemblages, and in particular to trait similarity between different biotas [5]. We define here species assemblages as the sets of species whose range maps intersect with grid cells defined at 200x200 km resolution. We investigate how much the similarity of species niche-related traits between assemblages (i.e. trait β-diversity) differs from expected similarities assuming a neutral model of evolution. Theory predicts that trait convergence (or divergence) events at the species level scale-up to entire assemblages if multiple pairs of convergent (or divergent) species show the same geographical distribution [5,23,24]. For example, if two independent adaptive radiations occurred in two different regions, so that the same ecological/functional guilds independently evolved in the two clades of the two regions, we would expect to find high trait similarity between these regions (low trait β-diversity) despite the differing evolutionary backgrounds (i.e. assemblage convergence) [24]. In this case, multiple species-level convergence events do scale up to trait convergence between entire assemblages. While there are a few published examples for small clades [2527], evidence of evolutionary trait convergence at the scale of entire biotas is mostly qualitative [5].

We scaled up our species-scale analysis to the assemblage scale using global species distribution data. We tested for assemblage convergence and divergence by extending our species scale trait distance metric to an assemblage scale trait β-diversity metric [(observed trait β – mean expected trait β) / standard deviation of expected trait β]. Expected trait β-diversity was computed using the simulated trait data previously used for the species-scale analysis. This phylogenetically standardized trait β-diversity measures the extent to which observed trait β-diversity was lower (convergence) or higher (divergence) than expected under neutral evolution (see Supplemental Experimental Procedures for details). We found that most pairs of assemblages (83%) show trait similarity that does not differ from expectations based on neutral evolution. However, many pairs of assemblages showed strong signatures of trait convergence: 13% (12-16% when using alternative evolutionary model parameters of the Markov model, see Supplemental Experimental procedures) of all pairs of assemblages showed lower functional trait distances than expected under BM (orange dots in Figure 2). In contrast, the signature of assemblage divergence was less pronounced with only 4% (4% when using alternative parameters, see Supplemental Experimental procedures) of all pairs of assemblages showing significant divergence (blue dots in Figure 2).

Figure 2. Relationship between the phylogenetically standardized trait β diversity and climatic distances between assemblages.

Figure 2

Deviations of observed trait β diversity from a neutral model of evolution (i.e. phylogenetically standardized trait β diversity) are plotted against climatic distances between assemblages worldwide (for the purposes of clarity, only 50,000 assemblage pairs are represented). Climatic distances are Euclidian distances between assemblages in the climatic space of the two first axes of a PCA of 19 bioclimatic variables. Solid lines show mixed model fit (slope estimate 0.17; 95% CI: 0.16-0.17, fitted on 200 stratified grid cells, see Supplemental Experimental Procedures and Figure S4). If the observed trait β diversity between two assemblages is significantly lower (higher) than neutral expectations, points are shown in orange (blue). See also Figures S2-4.

If convergent evolution at the global scale is driven by natural selection, we expect evolutionary convergent assemblages to occur in similar climatic conditions. This hypothesis predicts that phylogenetically standardized trait β-diversity is lower between assemblages that experience similar climatic conditions, and that it increases when the climatic distances between assemblages increase. We globally found a positive and significant relationship between phylogenetically standardized trait β-diversity and climatic distance (slope mean estimate 0.17; 95% CI: 0.16-0.17; Figure 2), indicating that the convergence of assemblages significantly increased with climate similarity. To make sure our results were driven by a general tendency across clades and traits, we re-estimated this relationship while (i) removing some important mammalian clades (i.e. Rodentia, Chiroptera, Soricomorpha, Primates, Carnivora, Diprotodontia and Artiodactyla, see Figure S2A-H), (ii) keeping all combination of only three out of four broad trait categories (Figure S3A-D) and (iii) bootstrapping trait items within broad categories (Figure S3E, Table S3 and Supplemental Experimental procedures). We further assessed the sensitivity of our results to the neutral models used by re-estimating the climate-convergence relationship with other parametrizations and choice of models (Figure S3F-H). In addition, we used ordination techniques to produce a composite trait axis that was subsequently used to test for a potential bias related to the fact that the correlation between observed traits was not taken into account in our initial neutral model (see Supplemental Experimental Procedures, Table S2 and Figure S3I-J). All these sensitivity analyses demonstrate that our results are (i) robust to the way neutral models of evolution are calibrated and defined and (ii) generalizable across clades and traits. Therefore, our results represent an emergent property of mammalian distribution and evolution, and support the hypothesis that natural selection was important in shaping the evolutionary and geographical patterns of mammalian trait diversity.

Finally, to identify which regions contribute most to the convergent and divergent patterns, we spatially mapped the extreme convergent and divergent pairs of assemblages. In order to visualize the degree of assemblage convergence for each assemblage, we averaged, for each grid-cell in the world, its standardized trait distance value to all other cells of the world. Australia harboured assemblages that exhibit the highest levels of assemblage trait convergence (Figure 3). Extremes of assemblage convergence are evident between, for example, Australia and North temperate regions or Africa (Figure 4 and Supplemental GIF). Importantly, this result is recovered across all our sensitivity analysis (Figure S2-3), demonstrating that Australia shows a strong and recurrent pattern of convergence. This is due to the fact that Australia has experienced multiple adaptive radiations during its long geological isolation [2830]. In particular, Australia’s mammalian fauna is dominated by marsupials, a clade for which we found strong similarities with placental species in the species-level analyses (Figure 1 and S1) and that significantly contributes to the extreme Australian assemblage convergence (Figure S2K). Thereby, our results provide quantitative evidence for the long-standing hypothesis of assemblage scale trait convergence between the Australian marsupial and the North temperate placental biota [5]. However, the extreme convergence found in Australia is not only restricted to marsupials, but is also driven by other clades (e.g. native rodents, Figure S2I-J). This result reflects the fact that Australia harbours a unique fauna within which convergence with other faunas of the world has occurred repeatedly through evolutionary time, and is not restricted to one particular clade [29,30]. Interestingly, we did not recover extreme cases of assemblage convergence in Madagascar, while it is known that it occurred in some endemic groups to the island (e.g. Tenrecs). This is likely because these groups do not represent the majority of species within the assemblages, so that the species level convergences do not scale up to entire assemblages.

Figure 3. Spatial patterns of global assemblage scale convergence and divergence.

Figure 3

This map represents the global distribution of phylogenetically standardized trait β diversity averaged by grid cell (i.e. for a given grid cell, pairwise trait β diversity values are averaged across all other grid cells in the world). Red (/blue) colours indicate assemblage convergence (/divergence).

Figure 4. Spatial patterns of extremely convergent and divergent pairs of assemblages.

Figure 4

These maps represent the global distributions of pairs of assemblages with the top 0.25 % of the highest negative phylogenetically standardized trait β diversity (i.e. assemblages that converge much more than expected under neutral evolution, panel A) and pairs of assemblages with the top 0.25% of the highest positive phylogenetically standardized trait β diversity (i.e. assemblages that diverge much more than expected under neutral evolution, panel B). Filled circles represent assemblages and circle diameter relates to the number of times a given assemblage is found in the top 0.25% convergent (panel A) or divergent (panel B) pairs. See also Figure S2-4.

The spatial pattern of the most divergent assemblages involved the artic region (Northern North America and Greenland) and tropical or temperate zones in different continents (e.g. southern Eurasia or Southeast Asia, see Figure 4) and is generated by species that inhabit the arctic and have close relatives in temperate or tropical regions with divergent trait characteristics. Significantly divergent pairs of assemblages were much less common than convergent ones (4% vs. 13%) and mostly concerned species poor assemblages adapted to climatically extreme or narrow environmental conditions (e.g. arctic regions).

In this study, we showed that natural selection of mammalian traits influences the trait structure of entire assemblages at the global scale and, in particular, the assemblage scale convergence of between the Australian and Eurasian, North American and African faunas. While these convergences are measured here in terms of coarse scale niche-related traits, it is likely that they emerge from multiple finer scale morphological, behavioural and physiological convergent traits. For example, the independent emergence of large herbivores in Marsupialia and Placentalia (e.g. kangaroos and deers) is also associated with convergent physiological and anatomical traits not measured in this study (e.g. rumination), even in the absence of strong morphological convergences. Throughout our analysis, we argued that the assemblage-scale trait convergences detected resulted from repeated species-level evolutionary convergence events, i.e. in-situ adaptive evolution (ISE) in distinct regions [27,31]. However, deviations from evolutionary neutral expectations may also arise in other evolutionary and biogeographical scenarios, for example an ecologically conservative dispersal process [27,31] (ECD). In this scenario, (1) some lineages harbour less trait distance than expected under a neutral model of evolution because of trait conservatism [20] and (2) dispersal events allow these lineages to colonize different assemblages (e.g. when the two sister species are allopatric). Trait conservatism occurs when, for example, the traits of two sister species have evolved very slowly (or not at all) since their last common ancestor. Clades that evolved more slowly than the rate averaged over the entire mammal phylogeny will harbour lower trait distances than predicted under our single rate BM model. If some assemblages are mainly composed of species that belong to those clades with relatively low rates of trait evolution and also have high dispersal abilities, we would find trait similarity between these assemblages to be much lower than expected under BM, and they would be detected as ‘convergent’ by our approach. For example, bats, which show high trait conservatism (Figure 1), are widespread across the globe and contribute to the high convergence in Australia (Figure S2L). The scope of our analysis and the methods used are not designed to disentangle the relative contributions of ISE and ECD to the globally observed assemblage convergence. Future research needs to explicitly relate the timing of trait evolution to colonization and diversification in distinct geographic regions [27,31], to be able to measure the relative contribution of the two processes or, alternatively, to explicitly take into account rate variations across the mammal tree. Nevertheless, our results strongly support that, at the global scale, niche-based processes play an important role in structuring the trait composition of mammal assemblages, either by directly triggering convergent trait evolution (ISE hypothesis), by environmental filtering of lineages experiencing niche conservatism (ECD hypothesis), or by both processes. We acknowledge that our estimates of convergent and divergent assemblage pairs proportions are the result of the two processes and that it remains complicated to tease apart their relative importance. Additionally, our approach does not take into account trade-off between traits, which might bias our result toward an overestimation of convergence. Nevertheless, sensitivity analysis show that the most extreme cases of convergent assemblages detected in this study involved Australian vs. Eurasian/North American assemblages (Figure 3-4, Figures S2-3). In this particular case, historical dispersal between assemblages was low, suggesting that the ISE hypothesis is more likely. Therefore, our work supports the long-standing hypothesis of convergence between the Australian and North temperate faunas, both at the species and at the assemblage level.

Supplementary Material

Supplementary Materials

Acknowledgements

The research leading to these results received funding from the European Research Council under the European Community’s Seven Framework Programme FP7/2007-2013 Grant Agreement no. 281422 (TEEMBIO). All authors belong to the Laboratoire d’Écologie Alpine, which is part of Labex OSUG@2020 (ANR10 LABX56). ROW received funding from the Swiss National Science Foundation (grant 147226). All computations presented in this paper were performed using the CIMENT infrastructure (https://ciment.ujf-grenoble.fr), which is supported by the Rhône-Alpes region (GRANT CPER07_13 CIRA: http://www.ci-ra.org) and France-Grille (http://www.france-grilles.fr). FM would like to thank Karel Mokany, Laura Pollock and Mathieu Groussin for comments on a previous version of the MS.

Footnotes

The authors declare no conflicts of interest.

Author contributions

JR formatted the distribution data. FM conceived the study, with advices from SL, ROW and WT. FM performed all analyses, with help of ROW and MG. FM interpreted the results with help of ROW, GFF, SL and WT. FM & WT wrote the first version of the manuscript and all authors contributed to revisions.

Contributor Information

Florent Mazel, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France.

Rafael O. Wüest, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France Swiss Federal Research Institute WSL, Landscape Dynamics, CH-8903 Birmensdorf, Switzerland.

Maya Gueguen, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France.

Julien Renaud, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France.

Gentile Francesco Ficetola, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France; Department of Biosciences, Università degli Studi di Milano. Via Celoria 26, 20133 Milano, Italy.

Sébastien Lavergne, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France.

Wilfried Thuiller, Univ. Grenoble Alpes, CNRS, Laboratoire d’Écologie Alpine (LECA), F-38000 Grenoble, France.

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