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bs_bs_banner Biological Journal of the Linnean Society, 2012, 107, 210–218. With 2 figures Colour-polymorphic snake species are older LIGIA PIZZATTO1 and SYLVAIN DUBEY2* 1 School of Biological Sciences (A08), University of Sydney, Sydney, NSW 2006, Australia Department of Ecology and Evolution, Biophore Building, University of Lausanne, 1015 Lausanne, Switzerland 2 Received 3 March 2012; revised 2 April 2012; accepted for publication 2 April 2012 bij_1936 210..218 Many characteristics, for example life-history traits, physiological tolerance to heat and cold, and energy requirements, contribute to a population’s ability to persist in the face of climatic variation. Recent studies have suggested that the presence of intraspecific colour polymorphism could be another potential contributor to population resilience (e.g. to climate change) in ectothermic vertebrates such as reptiles. In the present study, we tested for a relationship between the presence of intraspecific colour polymorphism and the age of snake species. Using phylogenetic comparative methods, we demonstrate that the presence of intraspecific colour polymorphism is correlated with the age of a species, with polymorphic snake species being significantly older than monomorphic species. Understanding how species have dealt with past environmental modifications, such as climate change, can provide important insights into how they are likely to respond in the future to continuing climate warming. © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218. ADDITIONAL KEYWORDS: climate change – colour polymorphism – intraspecific diversification – molecular dating – reptile. INTRODUCTION The coloration of an organism affects many facets of its existence, including fitness-relevant functions such as behaviour, thermoregulation, and metabolic physiology, as well as predator–prey interactions through mimicry, aposematism, and camouflage (Rosenblum, Hoekstra & Nachman, 2004; Roulin, 2004; Protas & Patel, 2008; McKinnon & Pierotti, 2010; Rosenblum et al., 2010). Consequently, colour polymorphism within a population and/or a species (in addition to parameters such as life-history traits, physiological tolerances, or energy requirements) may expand the range of environmental conditions under which at least some individuals are well suited to meeting local abiotic and biotic challenges (e.g. Theurillat & Guisan, 2001; Dirnböck, Dullinger & Grabherr, 2003; Jiguet et al., 2007; Forcada, Trathan & Murphy, 2008; Forsman & Aberg, 2008a; Huey & Tewksbury, 2009; Kearney, Porter & Shine, 2009; Caesar, Karlsson & Forsman, 2010; Dubey & Shine, *Corresponding author. E-mail: [email protected] 210 2011a). In addition, intraspecific colour polymorphism allows individuals to exploit different microhabitat types (e.g. Shreeve, 1990; Edelaar, Siepielski & Clobert, 2008), and allows different predator avoidance strategies (e.g. Proehl & Ostrowski, 2011). Thus, polymorphic populations may be more likely to successfully face present and future environmental modifications, such as current global warming, and modifications in, for example, predator pressure or food accessibility. Finally, body colour is likely to be especially significant for ectothermic animals, because of their reliance upon ambient conditions for thermoregulation (Clusella-Trullas, van Wyk & Spotila, 2007). For example, dark ectothermic organisms warm up faster than pale individuals, and are therefore able to boost their metabolism more rapidly under low-temperature conditions (Clusella-Trullas et al., 2007). Previous studies in owls have suggested that reddish individuals have a higher survival in warm– wet years than in cold–dry years. Reddish coloration (associated with pheomelanic pigments) may be linked with an ability to deal with warm climatic © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 COLOUR-POLYMORPHIC SPECIES ARE OLDER conditions, whereas a non-reddish coloration may be associated with greater success in colder climates (e.g. Gehlbach, 1986; Galeotti & Cesaris, 1996; Galeotti et al., 2003, 2009; Roulin, 2004; Roulin, Burri & Antoniazza, 2011). Roulin et al. (2011) suggested that climate change, which is currently more important at high latitudes, may have dramatic consequences in non-reddish species located near the poles, and that colour-polymorphic species (including reddish and non-reddish individuals) may be at an advantage because the presence of reddish individuals would lower the risk of extinction. Consequently, colourpolymorphic populations should be able to exploit wider niches than monomorphic populations, which may increase their resilience to extinction (Forsman et al., 2008; Forsman & Aberg, 2008a; Roulin et al., 2011). Similarly, the evolution of intraspecific colour polymorphism may have allowed ectothermic species to withstand past modifications of their environment, such as Pleistocene glaciations (1.8–0.012 Ma), more successfully than did otherwise similar monomorphic taxa. Polymorphic species may thus be expected to be older than monomorphic species because of the lower probability of historic extinctions (Forsman et al., 2008). In the present study, we tested this hypothesis by investigating the relationship between colour polymorphism (considering species with true withinpopulation polymorphism and species with variable colour patterns) and the age of snake species (the age of the oldest intraspecific diversification event, which is the minimum length of time since existing populations within a species last shared a common ancestor), by assembling data from published molecular phylogenies. MATERIAL AND METHODS AGE OF SPECIES AND COLOUR POLYMORPHISM We estimated the age of a species, as described in Dubey & Shine (2011b, 2012) and Weir & Schluter (2007), i.e. by using the oldest intraspecific diversification event (based on molecular dating) within each species (see Table 1). This measure estimates the minimum length of time since existing populations within a species last shared a common ancestor. We reviewed papers on phylogeny, polymorphism, and geographic distribution of 72 species of snakes around the world to test for a relationship between colour polymorphism and the age of taxa. We excluded data on known non-monophyletic taxa and, in order to avoid inaccurate species age estimations, only data from comprehensive phylogeographic and phylogenetic studies were included in the analyses. 211 Species were classified as being polymorphic (i.e. exhibiting at least two different colour morphs) or monomorphic based on field guides and previously published studies (Forsman & Åberg, 2008b; see Table 1). Sexually colour dimorphic species were considered as polymorphic only if polymorphism is present within at least one sex, otherwise they were considered as non-polymorphic, as in Forsman & Aberg (2008a, b). In addition, there is no reason to expect colour polymorphism to persist over evolutionary time, given that it is not always stable and hence may be transient through time (Gray & McKinnon, 2007; Cameron & Pokryszko, 2008; Forsman & Aberg, 2008a, b; Lepetz et al., 2009). Consequently, a polymorphic population could become monomorphic through the elimination of a morph, or it could develop into geographic variations (Hedrick, 2006; Forsman & Aberg, 2008a, b). Thus, no distinction was made between species considered as exhibiting geographic variation in coloration or within-population polymorphism (as in Forsman & Aberg, 2008a, b), and both types were classified as variable colorations. Similarly, morphs could have been extinct in past events, rendering a species monomorphic in our classification. However, we are unable to recognize such situations. ANALYSES From the initial 72 taxa, we had a complete data set for 67 species. Thus, we reconstructed a phylogenetic hypothesis for 67 snake species, from seven families (22 Viperidae, 22 Colubridae, ten Elapidae, nine Leptyphlopidae, one Typhlopidae, two Boidae, and one Homalopsidae), using cytochrome b sequences downloaded from GenBank and aligned by eye. For maximum likelihood (ML), models of DNA substitution were selected using the Bayesian Information Criterion (BIC; Schwarz, 1978) implemented in JMODELTEST 0.1.1 (Guindon & Gascuel, 2003; Posada, 2008). The model best fitting our data was the GTR + I + G. We performed ML heuristic searches using PHYML (Guindon & Gascuel, 2003). Sequences of Varanus komodoensis and Lacerta viridis were used to root the tree. Because no cytochrome b sequences of Typhlops vermicularis were available in GenBank, and as it was the only member of the family included in our data set, and we wished to retain it, we used the cytochrome b sequence of another species (Typhlops platycephalus) to perform the analyses. All statistical tests were run using various R routines (R Development Core Team, 2008). First, we tested for phylogenetic signal in the age (logtransformed) of species using the Blomberg’s K statistic (Blomberg, Garland & Ives, 2003), calculated © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 212 L. PIZZATTO and S. DUBEY Table 1. Raw data on the age of species (log-transformed), based on oldest intraspecific diversification events, as revealed by molecular phylogenies (with corresponding references), presence of colour polymorphism, and reproductive mode (viviparous or not) of the species used in the present study Species Age Polymorphism Viviparity References Agkistrodon bilineatus Agkistrodon contortrix Agkistrodon piscivorus Atropoides mexicanus Atropoides nummifer Atropoides olmec Bitis arietans Cerrophidion godmani Charina bottae Coluber constrictor Contia tenuis Coronella austriaca Crotalus aquilus Crotalus atrox Crotalus cerastes Crotalus lepidus Crotalus mitchellii Crotalus pusillus Crotalus ruber Crotalus tigris Diadophis punctatus Drysdalia coronoides Drysdalia mastersii Enhydris subtaeniata Gloydius brevicaudus Guinea bicolor Hoplocephalus bungaroides Hoplocephalus stephensii Lampropeltis getula Lampropeltis pyromelana Lampropeltis zonata Leptodeira nigrofasciata Leptotyphlops kafubi Leptotyphlops nigricans Leptotyphlops nigroterminus Leptotyphlops scutifrons Leptotyphlops sylvicolus Lichanura trivirgata Malpolon monspessulanus Masticophis flagellum Naja haje Naja katiensis Naja mossambica Naja nubiae Naja pallida Namibiana occidentalis Natrix maura Natrix natrix Natrix tesselata Nerodia erythrogaster Nerodia fasciata Nerodia rhombifer Nerodia sipedon Nerodia taxispilota Pituophis catenifer Pituophis deppei Pseudechis australis Sistrurus catenatus Sistrurus miliarius Thamnophis validus Tricheilostoma macrolepis Trimorphodon biscutatus Typhlops vermicularis Vipera ammodytes Vipera aspis Vipera berus -0.2924 0.1399 0.3979 0.0309 0.3320 0.1490 0.6021 0.7562 0.9217 0.7782 0.7505 0.7033 0.2765 0.1335 0.1847 0.3927 0.5682 -0.0223 -0.6778 -0.7212 0.8382 0.0969 -0.1549 0.1461 0.3284 0.0580 -0.0706 -0.0706 0.6911 0.7482 0.5263 0.8129 0.3590 1.1492 0.5699 1.3636 1.2430 0.8692 0.6767 0.9877 0.2430 -0.2676 0.3365 0.0374 0.4502 0.8129 0.7243 0.7782 0.8261 -0.0506 0.2330 0.2695 0.4329 -0.1675 0.5911 0.6628 0.7959 0.6522 0.1399 -0.5452 0.5423 0.9823 0.7924 0.6128 0.5623 0.1461 Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes No No Yes Yes Yes No Yes No No Yes Yes No No Yes No No Yes No No Yes Yes Yes Yes No No No No No Yes Yes Yes Yes Yes No Yes No Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes No Yes Yes No No No No No No No No No Yes No No No No No No No No No No No Yes Yes Yes Yes Yes No No No Yes Yes Yes No No No Yes Yes Yes M. E. Douglas et al., J. Biogeogr. 36, 1164–1180 (2009). T. J. Guhier, F. T. Burbrink, Mol. Phylogenet. Evol. 48, 543–553 (2008). T. J. Guhier, F. T. Burbrink, Mol. Phylogenet. Evol. 48, 543–553 (2008). T.A. Castoe et al., J. Biogeogr. 36, 88–103 (2009). T.A. Castoe et al., J. Biogeogr. 36, 88–103 (2009). T.A. Castoe et al., J. Biogeogr. 36, 88–103 (2009). C. E. Pook, et al., Mol. Phylogenet. Evol. 53, 792–807 (2009). T.A. Castoe et al., J. Biogeogr. 36, 88–103 (2009). Rodriguez-Robles et al., Mol. Phylogenet. Evol. 18, 227–237 (2002). F. T. Burbrink et al., Mol. Phylogenet. Evol. 47, 274–288 (2008). C. R. Feldman, G. S. Spicer, Mol. Ecol. 15, 2201–2222 (2006). X. Santos et al., Amphibia-Reptilia 29, 35–47 (2008). R. W. Bryson et al., J. Biogeogr. 38, 697–710 (2011). T. A. Castoe, et al., Mol. Phylogenet. Evol. 42, 193–212 (2007). M. E. Douglas, et al., Mol. Ecol. 15, 3353–3374 (2006). R. W. Bryson et al., J. Biogeogr. 38, 697–710 (2011). M. E. Douglas, et al., Mol. Ecol. 15, 3353–3374 (2006). R. W. Bryson et al., J. Biogeogr. 38, 697–710 (2011). M. E. Douglas, et al., Mol. Ecol. 15, 3353–3374 (2006). M. E. Douglas, et al., Mol. Ecol. 15, 3353–3374 (2006). F. M. Fontanella, M. E. Siddal, Mol. Phylogenet. Evol. 46, 1049–1070 (2008). S. Dubey, et al., Mol. Phylogenet. Evol. 56, 1119–1125 (2010). S. Dubey, et al., Mol. Phylogenet. Evol. 56, 1119–1125 (2010). V. Lukoschek et al., Ecol. Evol. 1, 330–342 (2011). L. Ding et al., Mol. Ecol. 20, 1905–1922 (2011). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). J. Sumner, et al., Conserv. Genet. 11, 747–758 (2010). S. J. Keogh et al., Conserv. Genet. 4, 57–65 (2003). R. A. Pyron, F. T. Burbrink, Mol. Ecol. 18, 3443–3457 (2008). F. T. Burbrink et al., Mol. Phylogenet. Evol. 60, 445–454 (2011). C. R. Feldman, G. S. Spicer, Mol. Ecol. 15, 2201–2222 (2006). J. M. Daza et al. Mol. Phylogenet. Evol. 53, 653–667 (2009). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). D. A. Wood, et al., Mol. Phylogenet. Evol. 46484–502 (2008). S. Carranza et al., J. Biogeogr. 33, 1279–1288 (2006). K. A. Nagy et al. J. Zool. Syst. Evol. Research 42, 223–233 (2004). C. E. Pook, et al., Mol. Phylogenet. Evol. 53, 792–807 (2009). W. Wüster et al., Mol. Phylogenet. Evol. 45, 437–453 (2007). W. Wüster et al., Mol. Phylogenet. Evol. 45, 437–453 (2007). W. Wüster et al., Mol. Phylogenet. Evol. 45, 437–453 (2007). W. Wüster et al., Mol. Phylogenet. Evol. 45, 437–453 (2007). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). D. Guicking et al., Biol. J. Linn. Soc. 87, 127–143 (2006). D. Guicking et al., Biol. J. Linn. Soc. 87, 127–143 (2006). D. Guicking et al., Biol. J. Linn. Soc. 87, 127–143 (2006). M. C. Brandley et al. Mol. Phylogenet. Evol. 57, 552–560 (2010). M. C. Brandley et al. Mol. Phylogenet. Evol. 57, 552–560 (2010). M. C. Brandley et al. Mol. Phylogenet. Evol. 57, 552–560 (2010). M. C. Brandley et al. Mol. Phylogenet. Evol. 57, 552–560 (2010). M. C. Brandley et al. Mol. Phylogenet. Evol. 57, 552–560 (2010). R. W. Bryson et al. J. Biogeogr. 38, 1570–1584 (2011). R. W. Bryson et al. J. Biogeogr. 38, 1570–1584 (2011). U. Kuch et al., Naturwissenschaften 92, 121–127 (2005). L. S. Kubatko et al., Syst. Biol. 60, 393–409 (2011). L. S. Kubatko et al., Syst. Biol. 60, 393–409 (2011). A. De Queiroz, R. Lawson. Biol. J. Linn. Soc., 95, 409–424 (2008). S. A. Adalsteinsson et al., Zootaxa 2244, 1–50 (2009). T. J. Devitt, Mol. Ecol. (2006) 15, 4387–4407 (2006). P. Kornilios et al., Amphibia-Reptilia 32 (2011): 351–363 S. Ursenbacher et al., Mol. Phylogenet. Evol. 46, 1116–1128 (2008). S. Ursenbacher et al., Mol. Phylogenet. Evol. 38, 546–552 (2006b). S. Ursenbacher et al., Mol. Ecol. 15, 3425–3437 (2006a). © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 COLOUR-POLYMORPHIC SPECIES ARE OLDER and analysed in the package ‘PICANTE’ (Kembel et al., 2010). As this analysis presented a highly significant phylogenetic signal (k = 0.098, PIC variance Z = -2.54, P = 0.001), we continued our analyses using phylogenetic comparative methods. We explored the relationships between presence/absence of colour polymorphism and the age of the species [log(oldest intraspecific diversification in millions of years)] using a phylogenetic generalized least squares model, which incorporates information about relatedness, provided as a phylogenetic tree, into the error term of a generalized least squares model (GLM), assuming a particular model of trait evolution (see Martins & Hansen, 1997). In our analyses, we assumed a Brownian model of evolution and the phylogenetic information was incorporated into the GLM (package ‘nmle’; Pinheiro et al., 2009), using the package ‘APE’ (Paradis, Claude & Strimmer, 2004). Because the age of a species can also be related to its geographic distribution (Weir & Schluter, 2007; Dubey & Shine, 2011b, 2012), we included the mean latitude and range covered (difference in latitude between the northern- and the southernmost known population) of the species as covariates in the analyses. Similarly, the reproductive mode (egg laying versus live bearing) and the mean snout–vent length (SVL) of the adults were also considered as covariates, as variations are present in our data set and could potentially have an impact on the ages of species. Non-significant variables were removed one by one from the models, and we selected the model with the lowest AIC as the model with the best fit (Crawley, 2007). The normality of the observed versus fitted residuals, and homogeneity of the variances, were examined through the visual inspection of plots and the fitted correlation line. RESULTS The phylogeny of the snake species used to perform the phylogenetic comparative analyses is shown in Figure 1. The best-fit model contained only reproductive mode and presence/absence of polymorphism (Akaike’s information criterion, AIC = 88.90, logLik = -40.45). None of the other variables had significant effects on the age of the species (all P > 0.13), and generated models with AIC ranging from 98.4 to 120.1. The age of a species was marginally correlated with reproductive mode (t = -1.87, P = 0.067, coefficient = -0.39) and was positively correlated with the presence of polymorphism (t = 3.13, P = 0.0026, coefficient = 0.30): older species tended to be oviparous (Fig. 2A), and were in general polymorphic (Fig. 2B). Several young species, such as Thamnophis validus, Nerodia taxispilota, Nerodia rhombifer, Crotalus cerastes, Crotalus tigris, Crotalus ruber, Crotalus 213 atrox, Guinea bicolor, Leptotyphlops kafubi, and most Naja species, are also monomorphic. However, other young species (e.g. Nerodia fasciata, Hoplocephalus stephensii, Drysdalia coronoides, Drysdalia mastersii, and Naja hage) are polymorphic, and the oldest species Leptotyphlops nigricans, Leptotyphlops scutifrons, and Leptotyphlops sylvicolus are monomophic (Table 1). DISCUSSION Our study reveals that the presence of intraspecific colour polymorphism is strongly correlated with the age of a species (i.e. the oldest intraspecific diversification event): polymorphic snake species are significantly older than monomorphic species. This result can be explained by the important ecological roles that colour variation plays in ectothermic species (e.g. thermoregulation, behaviour, and prey–predator interactions; e.g. Rosenblum et al., 2004, 2010; Clusella-Trullas, 2006; Clusella-Trullas et al., 2007). Moreover, it is likely that intraspecific colour polymorphism may promote the ecological success of taxa (Forsman & Aberg, 2008a; Roulin et al., 2011), and that polymorphic taxa may be able to exploit a larger diversity of habitat types. In addition, theory predicts that variable coloration enhances the rate of geographic range expansion (Forsman et al., 2008), and thus the capacity of species to colonize new habitats. Hence, polymorphism may allow species to successfully face novel environmental challenges, such as Pleistocene climate fluctuations (leading to the contraction and subsequent expansion of species; e.g. Dubey et al., 2006) or current global warming (e.g. Roulin et al., 2011). In Europe, adders (Vipera berus) and asp vipers (Vipera aspis) exhibit extensive intraspecific colour variation, including melanistic forms, probably as an adaptation to enhance rates of heat transfer while basking in cold areas (Monney, Luiselli & Capula, 1996). Genetic data suggest that these snakes persisted in European refugia more successfully than did most other taxa of reptiles and amphibians (i.e. not only in southern European refugia, but also in central Europe; Ursenbacher et al., 2006a, b; Joger et al., 2007). Consistent with this finding, Forsman & Aberg (2008a) showed that Australian reptile species exhibiting colour polymorphism have broader distributions and exploit a higher number of habitat types. In addition, fewer polymorphic than monomorphic reptile species are represented among species currently listed as threatened in Australia (Forsman & Aberg, 2008a), and the same trend is true for Australian frogs (Forsman & Hagman, 2009). Similarly, in North American Squamates, polymorphic species tend to have more northerly geographic distributions, and © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 214 L. PIZZATTO and S. DUBEY Diadophis punctatus Contia tenuis Thamnophis validus Nerodia taxispilota Nerodia rhombifer Nerodia fasciata Nerodia sipedon Nerodia erythrogaster Natrix tesselata Natrix natrix Natrix maura Trimorphodon biscutatus Masticophis flagellum Coluber constrictor Coronella austriaca Lampropeltis pyromelana Lampropeltis zonata Lampropeltis getula Pituophis deppei Pituophis catenifer Leptodeira nigrofasciata Malpolon monspessulanus Enhydris subtaeniata Pseudechis australis Hoplocephalus bungaroides Hoplocephalus stephensii Drysdalia mastersii Drysdalia coronoides Naja haje Naja nubiae Naja pallida Naja katiensis Naja mossambica Cerrophidion godmani Atropoides lmec Atropoides mexicanus Atropoides nummifer Agkistrodon contortrix Agkistrodon bilineatus Agkistrodon piscivorus Gloydius brevicaudus Sistrurus miliarius Sistrurus catenatus Crotalus mitchelli Crotalus tigris Crotalus ruber Crotalus atrox Crotalus lepidus Crotalus aquilus Crotalus pusillus Crotalus cerastes Bitis arietans Vipera berus Vipera ammodytes Vipera aspis Charina bottae Lichanura trivirgata Typhlops platycephalus Guinea bicolor Tricheilostoma macrolepis Namibia occidentalis Leptotyphlops kafubi Leptotyphlops nigroterminus Leptotyphlops scutifrons Leptotyphlops sylvicolis Leptotyphlops nigricans Varanus komodoensis Lacerta viridis 0.5 Figure 1. Phylogeny of the 1113-bp cytochrome b gene in snake species, used in the phylogenetic comparative analyses with a maximum likelihood (ML) procedure and the GTR + I + G model of substitution. have more extensive geographic ranges (Forsman & Åberg, 2008b), suggesting that they are able to tolerate a broader range of environmental conditions and colder climates. What could explain the presence/maintenance of monomorphic species, given the advantage provided by colour polymorphism? Because colour polymorphism can lead to speciation events through, for example, reproductive isolation through sexual selection (see review of Gray & McKinnon, 2007), monomorphic species could be the result of relatively recent speciation events. In addition, we can expect © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 COLOUR-POLYMORPHIC SPECIES ARE OLDER 215 tropics (Weir & Schluter, 2007). Our results demonstrate that the age of a species is not only determined by external factors such as climatic variations, but also by the morphological characteristics of species, and how such characteristics allow species to deal with temporal or geographic variations in their environment. Finally, our results also suggest that there is a trend for egg-laying species to be slightly older that live-bearing species, a pattern that could be explained by an ancestral state of oviparity in Squamates (lizards and snakes). Indeed, (ovo-)viviparity evolved multiple times from oviparity as a result of abiotic and biotic selections in Squamates (e.g. Shine & Bull, 1979; Shine, 1983). In conclusion, understanding how species have dealt with climate change in the past can provide important insights into how they are likely to respond to climate change in the future. Based on our results, monomorphic species are likely to suffer more from future climate variations than are polymorphic taxa. ACKNOWLEDGEMENTS Figure 2. Differences in the ages of snake species [log(oldest intraspecific diversification in a million years)] according to their reproductive mode (A), and presence or absence of polymorphism (B). Circles represent averages and bars represent the standard errors of the raw values (i.e. not corrected for effects of phylogeny and covariates). that heterogeneous habitats favour colour polymorphism, through the optimization of crypsis through different processes for example (Gehlbach, 1988), whereas homogeneous habitats may prevent the evolution of colour polymorphism. Consequently, species living in such habitats are more likely to be monomorphic. Finally, species living in restricted areas may be less prone to exhibit colour polymorphism compared with widespread species (which occupy various habitat types; Forsman & Aberg, 2008a). Besides colour polymorphism, the age of a species is also correlated with differences in past climatic conditions. For example, Dubey & Shine (2011b, 2012) found that Northern Hemisphere amphibian and reptile taxa from temperate areas are younger than Southern Hemisphere taxa. This pattern probably results from the occurrence of more extreme Pleistocene glacial events in the Northern than in the Southern Hemisphere, potentially eliminating much of the then-existing biodiversity (e.g. Hewitt, 2000, 2003). Similarly, in birds and mammals, the age of species was younger at high latitudes than in the We thank W. Wüster, A. Forsman, D. G. Broadley, R. R. Pinto, and P. Passor for providing information about the presence of colour polymorphism in particular species, S. Keogh for providing DNA sequences of Hoplocephalus species, S. Blomberg for helpful tips on using R, A. Roulin, R. Tingley, and anonymous reviewers for providing helpful comments, and the Swiss National Science Foundation and the Australian Research Council for funding. REFERENCES Adalsteinsson SA, Branch WR, Trape S, Vitt LJ, Hedges SB. 2009. Molecular phylogeny, classification, and biogeography of snakes of the Family Leptotyphlopidae (Reptilia, Squamata). Zootaxa 2244: 1–50. Blomberg SP, Garland, T Jr, Ives AR. 2003. Testing for phylogenetic signal in comparative data: behavioral traits are more labile. Evolution 57: 717–745. Brandley MC, Guiher TJ, Pyron RA, Winne CT, Burbrink FT. 2010. Does dispersal across an aquatic geographic barrier obscure phylogeographic structure in the diamond-backed watersnake (Nerodia rhombifer)? Molecular Phylogenetics and Evolution 57: 552–560. Bryson RW, Garcia-Vazquez UO, Riddle BR. 2011. Phylogeography of Middle American gophersnakes: mixed responses to biogeographical barriers across the Mexican Transition Zone. Journal of Biogeography 38: 1570–1584. Burbrink FT, Fontanella F, Pyron RA, Guiher TJ, Jimenez C. 2008. Phylogeography across a continent: The evolutionary and demographic history of the North © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 216 L. PIZZATTO and S. DUBEY American racer (Serpentes: Colubridae: Coluber constrictor). Molecular Phylogenetics and Evolution 47: 274–288. Burbrink FT, Yao H, Ingrasci M, Bryson RW Jr, Guiher TJ, Ruane S. 2011. Speciation at the Mogollon Rim in the Arizona Mountain Kingsnake (Lampropeltis pyromelana). Molecular Phylogenetics and Evolution 60: 445–454. Caesar S, Karlsson M, Forsman A. 2010. Diversity and relatedness enhance survival in colour polymorphic grasshoppers. PLoS ONE 5: e10880. Cameron RAD, Pokryszko BM. 2008. Variation in Cepaea populations over 42 years: climate fluctuations destroy a topographical relationship of morph-frequencies. Biological Journal of the Linnean Society 95: 53–61. Carranza S, Arnold EN, Pleguezuelos JM. 2006. Phylogeny, biogeography, and evolution of two Mediterranean snakes, Malpolon monspessulanus and Hemorrhois hippocrepis (Squamata, Colubridae), using mtDNA sequences. Journal of Biogeography 33: 1279–1288. Castoe TA, Daza JM, Smith EN, Sasa MM, Kuch U, Campbell JA, Chippindale PT, Parkinson CL. 2009. Comparative phylogeography of pitvipers suggests a consensus of ancient Middle American highland biogeography. Journal of Biogeography 36: 88–103. Castoe TA, Spencer CL, Parkinson CL. 2007. Phylogeographic structure and historical demography of the western diamondback rattlesnake (Crotalus atrox): A perspective on North American desert biogeography. Molecular Phylogenetics and Evolution 42: 193–212. Clusella-Trullas S. 2006. Thermal ecology of melanistic and nonmelanistic species of cordylid lizards in the Western Cape of South Africa. Ph.D. Dissertation, Drexel University, Philadelphia, PA. Clusella-Trullas S, van Wyk JH, Spotila JR. 2007. Thermal melanism in ectotherms. Journal of Thermal Biology 32: 235–245. Crawley MJ. 2007. The R book, 942 pp. West Sussex: John Wiley & Sons, Ltd. Daza JM, Smith EN, Páez VP, Parkinson CL. 2009. Complex evolution in the Neotropics: The origin and diversification of the widespread genus Leptodeira (Serpentes: Colubridae). Molecular Phylogenetics and Evolution 53: 653–667. Devitt TJ. 2006. Phylogeography of the Western Lyresnake (Trimorphodon biscutatus): testing aridland biogeographical hypotheses across the Nearctic–Neotropical transition. Molecular Ecology 15: 4387–4407. De Queiroz A, Lawson R. 2008. A peninsula as an island: multiple forms of evidence for overwater colonization of Baja California by the gartersnake Thamnophis validus. Biological Journal of the Linnean Society 95: 409–424. Ding L, Gan XN, He SP, Zhao EM. 2011. A phylogeographic, demographic and historical analysis of the short-tailed pit viper (Gloydius brevicaudus): evidence for early divergence and late expansion during the Pleistocene. Molecular Ecology 20: 1905–1922. Dirnböck T, Dullinger S, Grabherr G. 2003. A regional impact assessment of climate and land-use change on alpine vegetation. Journal of Biogeography 30: 401–417. Douglas ME, Douglas MR, Schuett GW, Porras LW. 2006. Evolution of rattlesnakes (Viperidae; Crotalus) in the warm deserts of western North America shaped by Neogene vicariance and Quaternary climate change. Molecular Ecology 15: 3353–3374. Douglas ME, Douglas MR, Schuett GW, Porras LW. 2009. Climate change and evolution of the New World pitviper genus Agkistrodon (Viperidae). Journal of Biogeography 36: 1164–1180. Dubey S, Keogh JS, Shine R. 2010. Plio-Pleistocene diversification and connectivity between mainland and Tasmanian populations of Australian snakes (Drysdalia, Elapidae, Serpentes). Molecular Phylogenetics and Evolution 56: 1119–1125. Dubey S, Shine R. 2011a. Predicting the effects of climate change on an endangered montane lizard, Eulamprus leuraensis (Scincidae). Climatic Change 107: 531–547. Dubey S, Shine R. 2011b. Geographic variation in the age of temperate-zone reptile and amphibian species: southern Hemisphere species are older. Biology Letters 7: 96–97. Dubey S, Shine R. 2012. Are reptile and amphibian species younger in the Northern Hemisphere than the Southern Hemisphere? Journal of Evolutionary Biology 25: 220– 226. Dubey S, Zaitsev M, Cosson JF, Abdukadier A, Vogel P. 2006. Pliocene and Pleistocene diversification and multiple refugia in an Eurasian shrew (Crocidura suaveolens group). Molecular Phylogenetics and Evolution 38: 645–647. Edelaar P, Siepielski AM, Clobert J. 2008. PerspectiveMatching habitat choice causes directed gene flow: a neglected dimension in evolution and ecology. Evolution 62: 2462–2472. Feldman CR, Spicer GS. 2006. Comparative phylogeography of woodland reptiles in California: repeated patterns of cladogenesis and population Expansion. Molecular Ecology 15: 2201–2222. Fontanella FM, Siddal ME. 2008. Evaluating hypotheses on the origin and diversification of the ringneck snake Diadophis punctatus (Colubridae: Dipsadinae). Molecular Phylogenetics and Evolution 46: 1049–1070. Forcada J, Trathan PN, Murphy EJ. 2008. Life history buffering in Antarctic mammals and birds against changing patterns of climate and environmental variation. Global Change Biology 14: 2473–2488. Forsman A, Aberg V. 2008a. Associations of variable coloration with niche breadth and conservation status among Australian reptiles. Ecology 89: 1201–1207. Forsman A, Åberg V. 2008b. Variable coloration is associated with more northerly geographic range limits and larger range sizes in North American lizards and snakes. Evolutionary Ecology Research 10: 1025–1036. Forsman A, Ahnesjö J, Caesar S, Karlsson M. 2008. A model of ecological and evolutionary consequences of color polymorphism. Ecology 89: 34–40. Forsman A, Hagman M. 2009. Association of coloration mode with population declines and endangerment in Australian frogs. Conservation Biology 23: 1535–1543. Galeotti P, Cesaris C. 1996. Rufous and grey colour morphs © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 COLOUR-POLYMORPHIC SPECIES ARE OLDER in the Italian tawny owl: geographical and environmental influences. Journal of Avian Biology 27: 15–20. Galeotti P, Paleotti P, Rubolini D, Dunn PO, Fasola M. 2003. Colour polymorphism in birds: causes and functions. Journal of Evolutionary Biology 16: 635–646. Galeotti P, Rubolini D, Sacchi R, Fasola M. 2009. Global changes and animal phenotypic responses: melanin-based plumage redness of scops owls increased with temperature and rainfall during the last century. Biology Letters 5: 532–534. Gehlbach FR. 1986. Population and environmental features that promote adaptation to urban ecosystems: the case of Eastern screech-owls (Otus asio) in Texas. Acta XIV Congressus Internationalis Ornithologici 2: 1809–1813. Gehlbach FR. 1988. Population and environmental features that promote adaptation to urban ecosystems: the case of Eastern Screech-owls (Otus asio) in H. Ouellet (ed.), Acta 19 Congressus Internationalis Ornithologici. Volume 2. Ottawa, Canada: University of Ottawa Press, 1809–1813. Gray SM, McKinnon JS. 2007. Linking color polymorphism maintenance and speciation. Trends in Ecology and Evolution 22: 71–79. Guhier TJ, Burbrink FT. 2008. Demographic and phylogeographic histories of two venomous North American snakes of the genus Agkistrodon. Molecular Phylogenetics and Evolution 48: 543–553. Guicking D, Lawson R, Joger U, Wink M. 2006. Evolution and phylogeny of the genus Natrix (Serpentes: Colubridae). Biological Journal of the Linnean Society 87: 127–143. Guindon S, Gascuel O. 2003. A simple, fast, and accurate algorithm to estimate large phylogenies by maximum likelihood. Systematic Biology 52: 692–704. Hedrick PW. 2006. Genetic polymorphism in heterogeneous environments: the age of genomics. Annual Review of Ecology, Evolution, and Systematics 37: 67–93. Hewitt GM. 2000. The genetic legacy of the quaternary ice ages. Nature 405: 907–913. Hewitt GM. 2003. Ice ages: their impact on species distributions and evolution. In: Rothschild LJ, Lister AM, eds. Evolution on Planet Earth. New York: Academic Press, 339–361. Huey RB, Tewksbury JJ. 2009. Can behavior douse the fire of climate warming? Proceedings of the National Academy of Sciences of the United States of America 106: 3647–3648. Jiguet F, Gadot AS, Julliard R, Newson SE, Couvet D. 2007. Climate envelope, life history traits and the resilience of birds facing global change. Global Change Biology 13: 1672–1684. Joger U, Fritz U, Guicking D, Kalyabina-Hauf S, Nagy ZT, Wink M. 2007. Phylogeography of western Palaearctic reptiles – spatial and temporal speciation patterns. Zoologischer Anzeiger 246: 293 –313. Kearney MR, Porter W, Shine R. 2009. The potential for behavioral thermoregulation to buffer ‘cold-blooded’ animals against climate warming. Proceedings of the National Academy of Sciences of the United States of America 106: 3835–3840. 217 Kembel SW, Cowan PD, Helmus MR, Cornwel WK, Morlon H, Ackerly DD, Blomberg SP, Webb CO. 2010. Picante: R tools for integrating phylogenies and ecology. Bioinformatics 26: 1463–1464. Keogh SJ, Scott IAW, Fitzgerald M, Shine R. 2003. Molecular phylogeny of the Australian venomous snake genus Hoplocephalus (Serpentes, Elapidae) and conservation genetics of the threatened H. stephensii. Conservation Genetics 4: 57–65. Kornilios P, Ilgaz C, Kumluta Y, Giokas S, FraguedakisTsolis S, Chondropoulos B. 2011. The role of Anatolian refugia in herpetofaunal diversity: an mtDNA analysis of Typhlops vermicularis Merrem, 1820 (Squamata, Typhlopidae). Amphibia-Reptilia 32: 351–363. Kubatko LS, Gibbs HL, Bloomquist EW. 2011. Inferring species-level phylogenies and taxonomic distinctiveness using multi-locus data in Sistrurus rattlesnakes. Systematic Biology 60: 393–409. Kuch U, Keogh JS, Weigel J, Smith LA, Mebs D. 2005. Phylogeography of Australia’s king brown snake (Pseudechis australis) reveals Pliocene divergence and Pleistocene dispersal of a top predator. Naturwissenschaften 92: 121–127. Lepetz V, Massot M, Chaine AS, Clobert J. 2009. Climate warming and the evolution of morphotypes in a reptile. Global Change Biology 15: 454–466. Lukoschek V, Osterhage JL, Karns DR, Murphy JC, Vori HK. 2011. Phylogeography of the Mekong mud snake (Enhydris subtaeniata): the biogeographic importance of dynamic river drainages and fluctuating sea levels for semiaquatic taxa in Indochina. Ecology and Evolution 1: 330–342. Martins EP, Hansen PS. 1997. Phylogenies and the comparative method: a general approach to incorporating phylogenetic information into the analysis of interspecific data. American Naturalist 149: 646–667. McKinnon JS, Pierotti MER. 2010. Colour polymorphism and correlated characters: genetic mechanisms and evolution. Molecular Ecology 19: 5101–5125. Monney JC, Luiselli L, Capula M. 1996. Body size and melanism in Vipera aspis in the Swiss Prealps and central Italy and comparison with different Alpine populations of Vipera berus. Revue suisse de Zoologie 103: 81–100. Nagy KA, Lawson R, Joger U, Wink M. 2004. Molecular systematics of racers, whipsnakes and relatives (Reptilia: Colubridae) using mitochondrial and nuclear markers. Journal of Zoological Systematic Evolutionary Research 42: 223–233. Paradis E, Claude J, Strimmer K. 2004. APE: analyses of phylogenetics and evolution in R language. Bioinformatics 20: 289–290. Pinheiro J, Bates D, DebRoy S, Sarkar D, R Core Team. 2009. NLME: linear and nonlinear mixed effects models. R Package Version 3: 1–96. Pook CE, Joger U, Stümpel N, Wüster W. 2009. When continents collide: Phylogeny, historical biogeography and systematics of the medically important viper genus Echis (Squamata: Serpentes: Viperidae). Molecular Phylogenetics and Evolution 53: 792–807. © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218 218 L. PIZZATTO and S. DUBEY Posada D. 2008. jModelTest: phylogenetic model averaging. Molecular Biology and Evolution 25: 1253–1256. Proehl H, Ostrowski T. 2011. Behavioural elements reflect phenotypic colour divergence in a poison frog. Evolutionary Ecology 25: 993–1015. Protas ME, Patel NH. 2008. Evolution of coloration patterns. Annual Review of Cell and Developmental Biology 24: 425–446. Pyron RA, Burbrink FT. 2008. Lineage diversification in a widespread species: roles for niche divergence and conservatism in the common kingsnake, Lampropeltis getula. Molecular Ecology 18: 3443–3457. R Development Core Team. 2008. A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. Available at: http://www. R-project.org Rodriguez-Robles JA, Stewart GR, Papenfuss TJ. 2002. Mitochondrial DNA-Based Phylogeography of North American Rubber Boas, Charina bottae (Serpentes: Boidae). Molecular Phylogenetics and Evolution 18: 227– 237. Rosenblum EB, Hoekstra HE, Nachman MW. 2004. Adaptive reptile color variation and the evolution of the Mc1r gene. Evolution 58: 1794–1808. Rosenblum EB, Rompler H, Schoneberg T, Hoekstra HE. 2010. Molecular and functional basis of phenotypic convergence in white lizards at White Sands. Proceedings of the National Academy of Sciences of the United States of America 107: 2113–2117. Roulin A. 2004. The evolution, maintenance and adaptive function of genetic colour polymorphism in birds. Biological Review 79: 815–848. Roulin A, Burri R, Antoniazza S. 2011. Owl melanin-based plumage redness is more frequent near than away from the equator: implications on the effect of climate change on biodiversity. Biological Journal of the Linnean Society 102: 573–582. Santos X, Roca J, Pleguezuelos JM, Donaire D, Carranza S. 2008. Biogeography and evolution of the Smooth snake Coronella austriaca (Serpentes: Colubridae) in the Iberian Peninsula: evidence for Messinian refuges and Pleistocenic range expansions. Amphibia-Reptilia 29: 35–47. Schwarz G. 1978. Estimating the dimension of a model. Annals of Statistics 6: 461–464. Shine R. 1983. Reptilian reproductive modes: the oviparityviviparity continuum. Herpetologica 39: 1–8. Shine R, Bull JJ. 1979. The evolution of live-bearing in lizards and snakes. American Naturalist 113: 905–923. Shreeve TG. 1990. Microhabitat use and hindwing phenotype in Hipparchia semele (Lepidoptera, Satyrinae): thermoregulation and background matching. Ecological Entomology 15: 201–213. Sumner J, Webb JK, Shine R, Keogh JS. 2010. Molecular and morphological assessment of Australia’s most endangered snake, Hoplocephalus bungaroides, reveals two evolutionarily significant units for conservation. Conservation Genetics 11: 747–758. Theurillat JP, Guisan A. 2001. Potential impact of climate change on vegetation in the European Alps: a review. Climatic Change 50: 77–109. Ursenbacher S, Carlsson M, Helfer V, Tegelström H, Fumagalli L. 2006a. Phylogeography and Pleistocene refugia of the adder (Vipera berus) as inferred from mitochondrial DNA sequence data. Molecular Ecology 15: 3425– 3437. Ursenbacher S, Conelli A, Golay P, Monney JC, Zuffi MAL, Thierry G, Durand T, Fumagalli L. 2006b. Phylogeography of the asp viper (Vipera aspis) inferred from mitochondrial DNA: evidence for multiple Mediterranean refugial areas. Molecular Phylogenetics and Evolution 38: 546–552. Ursenbacher S, Schweiger S, Tomovical L, CrnobrnjaIsailovical J, Fumagalli L, Mayer W. 2008. Molecular phylogeography of the nose-horned viper (Vipera ammodytes, Linnaeus (1758)): Evidence for high genetic diversity and multiple refugia in the Balkan peninsula. Molecular Phylogenetics and Evolution 46: 1116–1128. Weir JT, Schluter D. 2007. The latitudinal gradient in recent speciation and extinction rates of birds and mammals. Science 315: 1574–1576. Wood DA, Meik JM, Holycross AT, Fisher RN, Vandergast AG. 2008. Molecular and phenotypic diversity in Chionactis occipitalis (Western Shovel-nosed Snake), with emphasis on the status of C. o. klauberi (Tucson Shovelnosed Snake). Molecular Phylogenetics and Evolution 9: 1489–1507. Wüster W, Crookes S, Ineich I, Mané Y, Pook CE, Trape JF, Broadley DG. 2007. The phylogeny of cobras inferred from mitochondrial DNA sequences: Evolution of venom spitting and the phylogeography of the African spitting cobras (Serpentes: Elapidae: Naja nigricollis complex). Molecular Phylogenetics and Evolution 45: 437–453. © 2012 The Linnean Society of London, Biological Journal of the Linnean Society, 2012, 107, 210–218