The study of the factors that influence population connectivity and spatial distribution of genetic variation is crucial for understanding speciation and for predicting the effects of landscape modification and habitat fragmentation, which are considered severe threats to global biodiversity. This dual perspective is obtained from analyses of subalpine mountain species, whose present distribution may have been shaped both by cyclical climate changes over ice ages and anthropogenic perturbations of their habitats. Here, we examine the phylogeography, population structure and genetic diversity of the lacertid lizard Iberolacerta monticola, an endemism considered to be facing a high risk of extinction in several populations.
We analyzed the mtDNA variation at the control region (454 bp) and the cytochrome b (598 bp) loci, as well as at 10 nuclear microsatellite loci from 17 populations throughout the distribution range of the species.
According to nuclear markers, most sampling sites are defined as distinct, genetically differentiated populations, and many of them show traces of recent bottlenecks. Mitochondrial data identify a relatively old, geographically restricted lineage, and four to six younger geographically vicariant sister clades, whose origin may be traced back to the mid-Pleistocene revolution, with several subclades possibly associated to the mid-Bruhnes transition. Geographic range fragmentation of one of these clades, which includes lowland sites, is very recent, and most likely due to the accelerated loss of Atlantic forests by human intervention.
Altogether, the data fit a “refugia within refugia” model, some lack of pattern uniformity notwithstanding, and suggest that these mountains might be the cradles of new species of Iberolacerta. However, the changes operated during the Holocene severely compromise the long-term survival of those genetic lineages more exposed to the anthropogenic perturbations of their habitats.
Citation: Remón N, Galán P, Vila M, Arribas O, Naveira H (2013) Causes and Evolutionary Consequences of Population Subdivision of an Iberian Mountain Lizard, Iberolacerta monticola. PLoS ONE 8(6): e66034. https://doi.org/10.1371/journal.pone.0066034
Editor: Daniele Canestrelli, Tuscia University, Italy
Received: November 7, 2012; Accepted: May 6, 2013; Published: June 7, 2013
Copyright: © 2013 Remón et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This work was supported by grants REN2003-02931/GLO (Ministerio de Ciencia y Tecnología, Spain), PGIDIT03RFO10301PR and PGIDIT06RFO10301PR (Xunta de Galicia, Spain), awarded to Horacio Naveira. Nuria Remón was also funded by grant PTA2008-1366-P (Ministerio de Ciencia y Tecnología, Spain), awarded to Marta Vila. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
The Quaternary period is punctuated by a series of cyclic large glacial-interglacial climate changes, particularly intense in the northern hemisphere, primarily determined by parameters of the Earth’s orbit . Longer cold and predominantly dry periods in Europe alternate with others much shorter and warmer, whose effects on the evolution of species are strongly influenced by central and south high mountains (European Alpine system), and may vary considerably among different ecological and distributional groups . In principle, the influence of middle high mountains in shaping the changes of a species’ range should be comparatively small, yet the phylogeographic patterns at these lower sites (below the upper level of tree growth, i.e. at subalpine and forest zones) may be markedly different from those of alpine species, and serve for a better understanding of the conditions that ultimately lead to speciation . Vicariance episodes, so inextricably linked to these climate changes, bring up for consideration the effects of habitat fragmentation on the genetic properties of these populations, particularly with respect to their evolutionary potential and, with climate amelioration, their capacity to expand from refugia. Isolated populations resulting from fragmentation, especially if they become sufficiently small, must face both deterministic (edge and Allee effects) and stochastic threats (environmental and demographic) –, which determine minimum threshold densities and may eventually drive fragmented populations into “extinction vortices” , or “mutational melt-downs” .
Iberolacerta monticola (Boulenger 1905) is one of the species included in the Iberian rock-lizard group, whose phylogenetic relationships and evolutionary histories are relatively well known –. It is defined as “vulnerable” [B1ab(iii)] in the IUCN Red List of Threatened Species, according to its extent of occurrence (less than 20,000 km2), its distribution (severely fragmented), and the quality and extent of its habitat (in continuing decline) . Endemic to the NW quadrant of the Iberian Peninsula, it is nominally subdivided into I. monticola monticola, restricted to the Serra da Estrela in Portugal, within the Western Mediterranean region of the Peninsula, and I. m. cantabrica, distributed across a wide area in NW Spain, within the Atlantic biogeographic region, mainly at rocky habitats in subalpine and forest zones of the Cantabrian Mountain Range. The mean height of these mountains falls off considerably after the so-called Picos de Europa massif, and Sierras de Peña Prieta, Peña Sagra and Híjar, on entering Cantabria, which turns out to be a determinant feature of the eastern limit of the I. m. cantabrica distribution (Figure 1A). Western populations, however, can be found at downright lowland areas, most of them associated to patches of Atlantic forests in shady fluvial gorges of Galicia . Besides, whereas the species extends with no apparent discontinuities over vast areas of suitable habitat throughout the Cantabrian Mountains, it appears severely fragmented elsewhere, with evidences of ongoing range contraction and local population extinction –. On the other hand, glacial dynamics in the NW of the Iberian Peninsula ,  indicate that large parts of the current range of I. monticola at middle high altitude (in principle, most sites >700–1,000 m asl, meters above sea level) must have been unsuitable for the species during the last ice age, a situation that most likely took place repeatedly during the cyclical climate changes of the Pleistocene .
Localization of the samples and mitochondrial haplotypes of I. monticola at the NW of the Iberian Peninsula. B) Mapping on this geographical distribution of the Bayesian phylogenetic tree of the mitochondrial sequences. A geological time scale in millions of years is shown below. Abbreviations: L1– Lambre; L2– Mandeo; L3– Serra da Capelada; L4– Eume; L5– Sobrado; L6– Serra da Queixa; L7– Serra do Xistral; L8– Serra dos Ancares; L9– Serra do Courel; L10– Montes do Pindo; L11– Serra da Estrela; L12– Somiedo; L13– Leitariegos; L14– Ubiña; L15– Vegarada; L16– Peña Prieta; L17– Sierra de Gistredo. Limits and corresponding nouns of the main administrative divisions of the study area are indicated on the map. Labels marking the extent and situation of the main river basin (Minho-Sil) and the two main mountain systems (Cantabrian Mountain Range and Macizo Galaico-Leonés) of this area are also placed on the map. Numbers from 1 to 23 denote mitochondrial haplotypes, as in Figure 2. The tree is rooted using I. cyreni (see Fig. S1). Range between min and max posterior probability values (0.53–1.0) is indicated by color and width gradients (blue to red, and slim to thick). Support values obtained by four different methods of analysis for the major clades of I. monticola (II, III, IV-V, and VI) are shown at each node; namely, from left to right, Bayes posterior probability (×100), ML best trees in consensus (%), NJ-bootstrap (%), and equally MP trees (%). A hyphen was inserted instead of a numerical value whenever a particular method did not support the Bayesian topology.
Molecular data openly question the subspecific rank of the population from Serra da Estrela and, conversely, point out an unexpectedly high degree of differentiation between the populations of Galicia and the Cantabrian Range, but fail to produce conclusive evidence on the location of putative glacial refugia, or the eventual dispersal routes from them –, , . The present study is thus aimed first at depicting and understanding the phylogeographic patterns of the populations of I. monticola, which may have been shaped both by Pleistocene glacial cycles and Holocene habitat fragmentation. But then we would like to address several issues concerned with the conservation of this species, by assessing the effects of population decline on the levels of deleterious mutation load and evolutionary potential to respond to an ever-changing environment.
Sampling, Microsatellite Genotyping and mtDNA Sequencing
Sampling of I. monticola was designed to include a full representation of the known distribution of this species. Ethics approval of all procedures involving vertebrate animals is legally required under the Spanish legislation (Royal Decree 1201/2005 and Law 32/2007, on the protection of animals used for experimentation and other scientific purposes), which is a transposition of the European Directive 86/609/EEC. In agreement with article 18 and annexes VII and XI of the said Royal Decree, all animal procedures performed as part of the experimental work described in this paper have received prior and explicit approval from the competent authorities, defined in article 3e of the Law, and substantiated in the corresponding regulations of the Spanish autonomous communities. Thus, permissions for fieldwork and the concomitant experimental procedures were issued by the Xunta de Galicia, Junta de Castilla-León, and Principado de Asturias, in Spain, and, in application of an analogous transposition of the European Directive, by the Instituto da Conservação da Natureza in Portugal. Altogether, 316 lizards were genotyped, from 17 populations and 24 sites covering most of the species range (Table S1 and Fig. 1A). In every case, animals were quickly (<5 min) processed at the capture site and immediately released afterwards. Processing consisted of obtaining biometric data and collecting tail-tips, which were preserved in 96% ethanol for molecular studies. Genetic variation was analyzed at 10 nuclear (microsatellite) and two mitochondrial loci (cytb–cytochrome b, 570 bp; CR–control region, 453 bp), corresponding to position intervals 14,193–14,763 and 16,311–16,773, respectively, of the Lacerta viridis mitochondrial genome (GenBank acc. no. AM176577); for amplification details, see Table S2. Whereas mitochondrial data were obtained from all the visited sites, the microsatellite analysis was restricted to I. monticola populations, and then to 15 representative localities (Table S1; data deposited at Dryad: http://dx.doi.org/s2479). This is made explicit in this section, since two of the sampling sites happened to harbor not I. monticola, but a different, so far undescribed, new Iberolacerta taxon (see Results). DNA extractions from tissue samples and genotyping were carried out as described elsewhere . Both mitochondrial markers were bidirectionally sequenced for 5–10 specimens per locality, and electropherograms were visualized and aligned using CodonCode Aligner v. 3.5.7 (CodonCode Corporation). Newly reported sequences have been deposited in GenBank (acc. nos. HQ234877–HQ234900, and EF121827–EF121834; see also Table S1 for a full cross reference of haplotypes and GenBank accessions). Sequences from two other closely related Iberolacerta species, namely I. galani and I. martinezricai, were included in the analyses (GenBank acc. nos. EF121835, EF121836, HQ234882, HQ234901, HQ234902 and HQ234903). A sequence from I. cyreni (constructed from EF121834 and AY267232) was used as outgroup to root the phylogenies.
Microsatellite Data Analyses
The MicrosatelliteToolKit  was used to format data input for other software used in this work, as well as to obtain frequencies of heterozygotes, both observed (hobs) and expected under Hardy-Weinberg equilibrium (hHW), and numbers of alleles for each locus and population (na), together with the corresponding averages across loci for each population (Hobs, HHW, and ). Exact tests of Hardy-Weinberg equilibrium (HWE) for each sample were conducted with Genepop v. 4.0 . Genetic structure within populations was examined by the inbreeding coefficient (fIS, or FIS when averaged over all loci) . Randomization based tests carried out with the aid of Fstat v. 2.9.3  were used both to assess the significance of fIS (1500 randomizations, for each locus in each population), and possible non-random allelic associations between pairs of polymorphic loci (2100 permutations). The significance level of all these tests was adjusted by the sequential Bonferroni procedure . Fisher’s exact tests of genic differentiation for all pairs of populations were conducted with Genepop v. 4.0.
We checked the analyzed populations for evidence of recent bottlenecks using both Bottleneck v. 1.2.02  and M-ratio software . In the approach implemented in Bottleneck, a two-phase mutation model with 5% of multi-step changes was assumed, using 10,000 iterations, and Wilcoxon signed rank tests of significance. For the M-ratio test, the bottleneck hypothesis was tested under three different population scenarios, corresponding to different values of the mutation parameter θ (4Neµ), as in , namely θ = value estimated from the data, θ = 10, and θ = 0.5. See footnote at Table 1 for definitions, abbreviations and further methodological details.
Two geographically “blind” approaches (i.e., with no a priori assumptions about populations) were taken to visualize the similarities among multilocus genotypes. First, by constructing a UPGMA tree of individuals , based on pairwise allele-sharing genetic distances, and then by performing a factorial correspondence analysis (FCA). The matrix of allele-sharing distances  was obtained with the aid of the microsatellite analyser (MSA) v. 4.05 . The corresponding tree was generated by the Neighbor program in PHYLIP v. 3.6 , and then exported to Mega 4 , just for editing and printing purposes. FCA was carried out with Genetix v. 4.05.2 .
At the population level, we first constructed a neighbor-joining tree of the populations, based on Cavalli-Sforza & Edwards chord distance, DC, which performs best for reconstructing tree topologies in simulated microsatellite data . Support for tree nodes was obtained by bootstrapping loci 10,000 times. Bootstraps samples and chord distances were obtained with MSA. As a second approach at this level of organization, discrimination among populations was then inferred using the Bayesian assignment procedures implemented in the software Structure v. 2.1 . To identify the likely number of populations (k) within I. monticola, we used both the method suggested in the original Structure paper, based on scoring mean log likelihoods penalized by one-half of their variance (estimated “log probability of data”, L(k)), and the approach developed by Evanno et al. , based on the rate of change in the log probability of data between successive k values (Δk). We used an admixture model of genetic clustering with correlated allele frequencies, run for 50,000 generations after a burn-in of 100,000 generations, assuming that there were up to 14 possible partitions of the data (k = 2 to k = 16), and ran 10 parallel chains to estimate what number of genetic clusters had the highest probability. Membership coefficients of individuals to each of the clusters were plotted with Distruct v. 1.1 , with individuals ordered geographically, generally from the western to the eastern parts of the range.
Mitochondrial DNA Data Analyses
The topological congruence between the phylogenies obtained with the two markers was assessed by the incongruence length difference (ILD) test , , carried out with the aid of PAUP* v. 4.0 . Maximum parsimony (MP), neighbor-joining (NJ), maximum likelihood (ML) and Bayesian methods were used for reconstruction of mitochondrial phylogenetic trees. MP and NJ analyses were conducted in Mega 5 , which also provided several descriptive statistics (number of variable and parsimony informative sites, p-distances between sequences). MP trees were obtained using the Close-Neighbor-Interchange algorithm, with search level 3, and 100 random addition sequence replicates. The NJ tree was based on distances obtained by the Tamura-Nei model, allowing for a heterogeneous pattern among lineages and gamma-distributed rates among sites. The value of the gamma shape parameter (0.20) was obtained using a combination of ancestral sequence inference and maximum likelihood estimation , with the aid of GZ-Gamma (http://www.personal.psu.edu/nxm2/Software/gamma/gamma.zip), based on 10,000 bootstrap replicates. For ML, we first determined the model of sequence evolution that best fitted each of the four partitions of the data, namely (i) control region, (ii) 1st, (iii) 2nd, and (iv) 3rd codon positions of the cytb, by the Bayesian Information Criterion (BIC), using the metaPIGA v.2.1.3 development (http://www.metapiga.org)  of jModelTest . ML phylogeny for the combined mitochondrial dataset was estimated by consensus pruning (meta-population genetic algorithm), using default operators and parameters in metaPIGA, choosing the best-fit model selected by BIC for each partition (HKY85+ Γ, with the corresponding estimates of the shape parameter). We used loose Neighbor-Joining (20% range) to generate the starting trees, based on a HKY85 distance matrix, with rate heterogeneity across sites (shape parameter of the Γ distribution = 0.20). A ML test of the molecular clock hypothesis for the consensus topology thus obtained was carried out with Mega 5. As for the Bayesian phylogenetic inference, we used MrBayes v. 3.2 , , again specifying a HKY85+ Γ model for each of the four partitions of the data. The analysis was carried out with MrBayes default priors until the standard deviation of split frequencies dropped below 0.01, and the potential scale reduction factor for all parameters lied close to 1.0. Two simultaneous, completely independent analyses starting from different random trees were run. For the Markov chain Monte Carlo (MCMC) sampling of the target distribution, three heated chains and one cold chain were used. The first 25% samples from the cold chain were discarded as burn-in. We used Bayes factor comparisons to test several topological hypotheses. Marginal model likelihoods were estimated by the stepping-stone method; strength of the evidence in favor of the better model was then assessed by the magnitude of the log-difference, following Kass and Raftery . The strict clock model was tested against the non-clock model using an analysis similar to the previous one, by comparing the marginal likelihoods of the two models. For tree calibration and dating, we used a uniform prior from 6.5 to 8.5 My on the oldest split in the tree, corresponding to the separation of cyreni, and from 1.9 to 2.9 My on the monticola-galani-martinezricai split. These “hard” bounds are based on Carranza et al. (2004)  (see also , ), whose dating method, relying on a single calibration point, has been reported to underestimate the age of several genera of Lacertini, as well as the time for the separation of major lineages of Lacertidae . However, the estimates for the divergence of other, relatively younger, genera of Lacertini (including Iberolacerta) fall well within the 95% confidence intervals produced by nearly all the methods and models tested by Hipsley et al. (2009) . MCMC analysis was run using 1,000,000 generations. The output cladogram summarizing the trees was visualized with FigTree v. 1.3.1 . Mean ages and 95% highest posterior density intervals of mtDNA phylogroups are used as estimates of divergence times.
Since tree-building methods tend to resolve intraspecific gene genealogies poorly when the different mitochondrial types are separated by few mutations, and ancestral haplotypes are still present in the populations , a network was also generated through tcs v. 1.21  and its outcome compared to the previous phylogenies.
The Alignment Transformation EnviRonment (ALTER)  was used to obtain properly formatted input data for the different programs used in this part of the work.
Mantel Tests and Analysis of Molecular Variance
Genetic samples were separated into two groups, corresponding to a priori continuous or fragmented distributions of the species (see Fig. 1A). Pairwise genetic differentiation between populations within each group was estimated both by FST  and DC  statistics, based on microsatellite frequencies (obtained with MSA), and by φST  for corresponding mtDNA data (obtained as part of the analysis of molecular variance, described below). To evaluate the relative importance of philopatry and population fragmentation in predicting levels of genetic structure across the study region, we then conducted a series of Mantel tests  with the aid of ibdws v. 3.15 , using 10,000 matrix permutations to assess significance. These tests are essentially regression analyses of genetic distance (FST, FST/(1−FST) or DC) against geographic distance (linear or log-transformed) , , to determine whether genetic differences show a significant pattern of isolation by distance (IBD). In addition, we also examined the relationship of these same indices of genetic distance with the average number of mitochondrial nucleotide differences between populations (Π), obtained with Mega v. 4, considered as a proxy of historical population connectivity . All analyses were bootstrapped over population pairs (10,000 replicates) to generate 95% confidence intervals for r2. Geographical distance matrices were generated with GDMG v. 1.2.3 .
Using the same two groups of populations, an analysis of molecular variance (AMOVA) in Arlequin v. 3.5  was carried out. Numbers of different alleles between microsatellite haplotypes (amounting to weighted FST over all loci) were used to compute the distance matrix. Significance tests were based on 1,000 permutations.
Phylogenetic Analysis of Mitochondrial Haplotypes
The sequences of the two mitochondrial markers (CR and cytb) produced essentially similar phylogenetic signals (P = 0.8149, according to the ILD test), so that they were concatenated to produce a two-gene data set (1,024 bp, containing 162 variable and 75 parsimony informative sites). The null hypothesis of equal evolutionary rate throughout the ML tree was not rejected at a 5% significance level (P<0.878), and Bayes factor comparisons rendered very strong evidence in favor of a strict molecular clock (log-difference of 10 units), which was accordingly assumed for all the phylogenetic reconstructions. Two of the samples, a priori from I. monticola, showed an exceptionally large number of nucleotide differences as compared with the others (mean net p-distance = 2.2%; mean p-distance among the other I. monticola samples = 0.8%). They correspond to individuals from the Sierra de Gistredo, at the SW of the Cantabrian Mountain Range, which is part of those largely independent lesser mountain groups found in the province of León, to the south of the Minho-Sil river basin, and east from the Ancares-Courel groups (see Table S1 and Fig. 1A for geographic details). This region is in-between the known distributions of I. galani (to the south) and I. monticola (to the northwest). As shown at Figs 1B & S1, the samples from Gistredo form a distinct basal, statistically supported clade (denoted I), whose splitting took place ca. 1.6 Million years ago (Mya; 95% confidence interval 1.24–2.00), thus probably meriting the consideration of its full species or subspecies status (see discussion).
As far as I. monticola sensu stricto (i.e. excluding Gistredo) is concerned, the mitochondrial results indicate that the most recent common ancestor (MRCA) of their different haplotypes dates back to ca. 0.9 Mya (0.67–1.25). The samples from the Cantabrian Mountain Range (CAMOR) give rise to two basal haplotype clusters, with strong statistical support, namely Xistral-Courel-Ancares in Galicia, on the one hand (nominally corresponding to the western part of CAMOR; clade III at Fig. 1B), and the rest of the mountain range in León, Asturias and Cantabria (clade II), on the other. Clade III is by far the most rich in haplotype diversity (Fig. 2), particularly at Ancares, where several relatively old mitochondrial lineages coexist at the same sites. It is also worth mentioning, on this respect, that the samples from Xistral constitute a monophyletic group that separated roughly 0.5 Mya (0.27–0.72), and that no matter the method chosen for phylogenetic reconstruction, the single haplotype found at Courel is significantly included in one and the same of the three subclades that subdivide the Ancares sample, whose origin dates back to ca. 0.7 Mya (0.43–0.97). The high diversity of the system formed by these mountains stands in sharp contrast with the unexpectedly low diversity and close similarity of the haplotypes observed in the main (eastern) part of the Cantabrian Range (clade II), in spite of the high census size and the large extension occupied by the corresponding populations, without apparent geographic discontinuity among them (Table S1 and Fig. 1A). As for the populations not included in CAMOR, all of them from currently fragmented habitats at the western part of the species range, and collectively denoted as OCCIDENTAL (Fig. 1A), a major clade (V) is observed, which includes the generally only haplotype found in the three riparian habitats (Eume-Lambre-Mandeo) and the low mountains close to them (Capelada), from now on referred to as Artabrian Gulf samples (Fig. 2), in addition to a subclade encompassing Serra de Queixa, Sobrado (lowland) and an haplotype from the Mandeo river basin (Fig. 1B). The MRCA of these sequences dates back to ca. 0.4 Mya (0.19–0.62). The single haplotypes found at Pindo and Queixa-1, the two remaining northwestern populations, also began to diverge approximately 0.4 Mya (0.10–0.75). They are joined in a separate clade (VI) both by the MP and the Bayesian reconstruction, but its statistical support is relatively low (Fig. 1B). Marginal model likelihoods show rather strong evidence in favor of this topology, though, when we force this partition to be always present in the sampled trees (log-difference of 2.6 units). Finally, the haplotypes from Serra da Estrela, at the southwest limit of the current distribution of I. monticola, form another small clade (IV), which is most closely related to clade V, although the statistical support for this topology (favored by a very strong log-difference of 23 units in Bayes factors comparisons) is not conclusive (see Fig. 1B). Altogether, the topological relationships of clades II, III, IV-V and VI, remain uncertain and give rise to a basal polytomy in the mitochondrial evolution of I. monticola, with clear geographic correlates, as shown in Fig. 1.
Circle size reflects the frequency of each haplotype. Small black circles indicate haplotype states that are necessary intermediates but are not present in the sample. Each line represents a single mutational step connecting two haplotypes. CAMOR (Cantabrian Mountain Range) and OCCIDENTAL refer to population assignments based on geographical localization.
Genetic Variation and Equilibrium Tests
A summary of the genetic variation observed at the different microsatellite loci and populations is given at Table S3 and Fig. S2. According to values of fIS and the corresponding tests for departure from HW equilibrium, four of the combinations locus x population show a significant excess of homozygotes at the 5% level (after Bonferroni correction), which might be due to segregating null alleles, namely A5 at Queixa-L6A, C113 at Courel-L9A, and PB20 at Courel-L9B and Leitariegos. Applying a conservative criterion, these data were not taken into account for estimating genetic distances among populations, nor for evaluating the evidence of past bottlenecks (see later). However, it should be mentioned that the number of positive fIS estimates for each locus and sample nearly doubles the number of negative estimates, and that only two negative global FIS scores were obtained for the different samples (see Table S3), thus indicating a general background of homozygote excess, probably associated to population structure (see discussion). Tests of gametic disequilibrium produced no significant result for any pair of loci.
Identification of Genetically Distinctive Clusters
According to Fisher’s exact test, all the sampled populations, except Eume and Capelada, show significantly different gene frequencies at microsatellite loci (P<0.0001). On the other hand, individuals from each locality generally group together in a UPGMA tree based on allele-sharing distances (Fig. 3). The reconstruction of the phylogenetic relationships among these populations by the NJ algorithm, using multilocus chord distances, lacks the necessary resolution to obtain significant support for most clusters, though (Fig. 4A). Most important, an internal branch separating CAMOR together with the “occidental” Estrela (CAMOR+E) from the rest of the OCCIDENTAL group (now formed entirely by northwestern populations, NWP), is observed at 73% of the bootstrap samples (see also Table S1 and Fig. 1). Factorial analysis identifies a main axis of variation corresponding to the separation between these same two groups of populations (axis 1 at Fig. 5, explaining 19.13% of total variation), with Estrela and Xistral being the populations of the first group nearest to the second, and a rather good correspondence with the distribution of populations along a longitudinal east-west transect (with negative values for the NWP group, and progressively higher positive values eastwards, for populations within CAMOR+E). The second axis (explaining 15% of total variation) effectively separates three subgroups within the NWP group (namely, Sobrado, Artabrian Gulf+Queixa, and Pindo). Bayesian analysis with Structure unveils a clear hierarchy in the partition of population samples among clusters (Figs 4B & S3), which agrees quite well with these FCA results and the former phylogenetic reconstruction obtained with NJ. The most likely number of clusters is 12, using either L(k) or Δk as optimization criterion (Fig. S4), which in fact means that each sample is assigned to a genetically differentiated population, with the sole exceptions of Eume-Capelada and Lambre-Mandeo, i.e. the Artabrian Gulf samples. At the most basic level (k = 2, thus forcing the subdivision of samples into two clusters), CAMOR+E and NWP groups become apparent (Figs 4B & S3). It is noteworthy that the individuals from Serra da Estrela are assigned to an exclusive cluster not until k = 7, being so far grouped together with the samples from Ancares and Courel (see also Fig. 3, for a similar grouping after UPGMA). Generally, more than 70% of the individuals collected at a given locality are assigned to the same cluster, under each of the different levels of structuring examined. The samples from Ancares, on the one hand, and Eume-Capelada, on the other, are exceptional on this respect, since their proportions of membership are sometimes relatively low (Fig. 4B).
A) Unrooted NJ tree, using chord distances. Numbers indicate bootstrap support (10,000 samples; only values ≥60% are reported) for the corresponding internal branches. B) Assignment of individuals from the predefined populations to k clusters, as inferred by STRUCTURE. Colors identify the different clusters inferred by the analysis. Log probabilities of data, L(k), together with % of parallel runs supporting the displayed partition, are shown for each k. Abbreviations: CAMOR– Cantabrian Mountain Range; NWP– North Western Populations (i.e., all those included in the occidental group, except Estrela).
Signatures of Fluctuations in Population Size
As regards the demographic history of these populations, the results of Bottleneck and M-ratio tests are shown in Table 1. Eight of the fourteen statistical populations show heterozygosity excess over mutation-drift expectations, which is highest for Pindo (10.6%) and then for Lambre (5.3%), but not statistically significant in either case. The M-ratio test, however, produced highly significant results for both these populations, as well as for Sobrado, Queixa, Courel-L9B and Vegarada. Using the least restrictive conditions for significance of this test (i.e., comparing observed m values with those expected using the value of θ estimated from the corresponding data), all the populations except Eume, Xistral, Ancares, Estrela and Leitariegos, show traces of recent bottlenecks.
Correlation of Genetic and Geographic Distance Measures
In principle, all CAMOR populations should be connected by gene flow, since no apparent geographical or ecological barrier has been found within their range (see Figure 1A), whereas all the other samples, grouped under the geographic tag of OCCIDENTAL, were obtained from populations nowadays isolated by habitat fragmentation. Independently of this “a prioristic” difference in connectivity, correlations of microsatellite genetic distance with geographical distance (unmodified for potential barriers) were always positive, as expected under a pattern of IBD (see Table 2), although there were clear asymmetries in the performance of the different indices in the two groups of populations. Similar results were obtained in the analysis of association of microsatellite distance with the proxy of historical population connectivity (average number of mitochondrial nucleotide differences between populations, Table 2). The frequent observation of a single and the same haplotype in several of the surveyed populations (see haplotypes 1 and 10, at Fig. 2) precluded IBD analyses using φST-based distances. This finding, together with the clear geographic subdivision of the genetic diversity of I. monticola (and the ensuing reduction of sample sizes), also hindered any attempt to infer the demographic history of its different lineages by mismatch-distribution analyses of pairwise mtDNA differences.
Genetic Consequences of Fragmentation and Reduced Population Size
Results from a two-way AMOVA indicate that most of the observed microsatellite variation is explained by differences within populations (80.5% of total variance, P<0.000001). Lower values are related to differences among populations within groups (14.5% of total variance, P<0.000001), and still lower to differences among groups (CAMOR vs. OCCIDENTAL, 5.0% of total variance, P = 0.00391). Results from several one-way AMOVAs, together with different measures of genetic diversity in continuous and fragmented populations are shown in Table 3. While both of these groups harbor similar levels of genetic variation at microsatellite loci, the among-populations component is estimated to be higher at OCCIDENTAL (18%, as compared with 11% at CAMOR), but the difference is not statistically significant. As for genetic diversity, all the scores are lower for OCCIDENTAL, both in terms of mean number of alleles per locus and mean heterozigosity within populations (see Table 4). However, as shown in this same table, all these observations arise not from the fragmented condition of these populations, but from the reduced size of most of them. Variation among fragmented populations of reduced size (OCCIDENTAL_R) is 100% higher than among continuous populations, as measured by the FST score (0.215 vs. 0.107), whereas the mean number of alleles per locus and expected heterozygosis at HWE are considerably lower in them (by a 34% and a 18%, respectively). Actually, OCCIDENTAL_R shows lower average numbers of alleles in 10 out of the 11 loci analyzed, and lower heterozygosis in nine of them (Table 4; P = 0.0024 and P = 0.0068, respectively, after Wilcoxon signed rank-tests). In addition, on average, large populations show an excess of homozygotes over HW expectations in a significant proportion of loci (P = 0.0087, one-tail Wilcoxon signed rank-test); this observation is consistent with mean FIS scores for these categories, which can be easily obtained from Table 1, namely 0.018 and 0.060 for reduced and large populations, respectively). Finally, θ estimates derived from mean expected heterozygosis point out a reduction of 48% in the scores obtained from reduced populations (1.62), as compared with large populations (3.10), which, assuming equal mutation rates in both classes, amounts to an equivalent descent in their corresponding mean effective population sizes.
Iberian Rock-lizards Speciation
Comparative phylogeographic analyses have shown strong genetic subdivisions, indicative of extended periods of population isolation, for many species and species complexes in the Iberian Peninsula, and especially for those with limited effective dispersal that live in mountains. This is most likely due to their survival throughout the Pleistocene ice ages in multiple refugia or sanctuaries, which tend to occur in mountain ranges , . Iberian rock-lizards (Iberolacerta spp.; phylogenetic revision in  and ) offer some good examples of this evolutionary pattern –, . Two recently described species, namely I. martinezricai (see , ) and I. galani , have a restricted montane distribution not far away from I. monticola populations (see Fig. 1). But the list of Iberolacerta species or subspecies in this region may not be exhausted. The denomination of Montes de León brings together a number of largely independent mountain groups, which constitute a perfect scenario for the emergence of parapatric genetic lineages. The mitochondrial results from the Sierra de Gistredo offer the first evidence on this respect, pointing out the existence of a clade clearly distinct from the three other species, whose independent evolution began roughly 1.6 Mya, at Early Pleistocene. Additional evidence from morphology (biometry and scalation), karyology and osteology, will be necessary to establish the definitive taxonomic status of this population, together with microsatellite data to investigate its genetic structure (in preparation).
Phylogeography of Iberolacerta monticola Populations
The mitochondrial results are consistent with the simultaneous vicariance of not less than four, and a maximum of six populations after the mid-Pleistocene revolution (about 0.9 Mya), one of the two major climate transitions of the Quaternary period, with drastic effects on the geographical distributions of many species –. In fact, several of the modern populations of the species reside in areas that have been suggested to serve as glacial refugia, on the basis of the distribution of many different plant and animal species (namely Serra da Estrela, and the western and eastern parts of the Cantabrian Mountain Range , ). Thus, the often-cited subdivision of I. monticola into I. m. monticola at Serra da Estrela, and I. m. cantabrica elsewhere, falls too short to describe the actual pattern of diversification within this species. With the conspicuous exception of Serra de Ancares, which shows extensive mitochondrial admixture, most other populations are characterized by parapatrically distributed clades and subclades. According to their estimated coalescence times, this pattern could be the outcome of the relatively recent (re)colonization of these areas from different refugial populations, which, as in other well documented cases , , have persisted without admixture during several ice ages. So the partition of Ancares-Courel vs. Xistral (clade III) in the CAMOR group, or the low-altitude Artabrian Gulf vs. the moderate-high altitude populations of Serra da Queixa (clade V) in the OCCIDENTAL group, whose dating (mean node ages of 0.4–0.5 Mya) agrees quite well with the second distinct climate change of the Quaternary, the mid-Bruhnes event, about 0.43 Mya .
The primarily east-west orientation of the Cantabrian Range may have facilitated the survival of populations simply by moving up or down mountains, as the general climate worsens or ameliorates . In this scenario, the model of “refugia within refugia”, put forward to explain the phylogeographic patterns observed for a range of fauna and flora in the Iberian Peninsula , offers a good frame for all our findings. In general, deeper intraspecific lineages are expected in populations whose range included several glacial refugia (that could be Ancares), whereas shallower and relatively impoverished lineages are expected for populations resulting from recent recolonization events (as found elsewhere). The impoverished mitochondrial diversity observed in the eastern clade (II), which includes the most widespread and largest I. monticola populations, might also be explained by a recent selective sweep, as suggested in other cases , . But even so, the relatively old origin of this clade would demand an explanation involving the interaction of selection and gene flow . Fine-scale analyses of the putative hybrid zones, involving nuclear markers (see ,  for a similar case in Lacerta schreiberi), will be necessary for a more thorough understanding of the evolution of these populations, which undoubtedly have experienced multiple episodes of admixture.
On general grounds, perhaps the main factor determining the level of genetic and regional subdivision of species inhabiting European mountains is the duration of the cycles of range contraction and expansion triggered by climate changes. For species dwelling at upper elevation (alpine) habitats, vicariance events are most likely associated to warm, relatively short interglacials, thus giving rise to shallow phylogenies. On the contrary, according to the displacement refugia model , species adapted to lower habitats are predicted to show stronger phylogeographic signals, due to prolonged fragmentation during the long glacial periods. The Pyrenean rock lizard Iberolacerta bonnali, which inhabits rocky habitats at 1,600–3,300 m asl, and whose current distribution is most likely a consequence of post-glacial range fragmentation after the end of the Last Glacial Maximum, would perfectly fit into the first category . Iberolacerta monticola should be expected to lie somewhere in-between the two extremes. Its mitochondrial lineages seem to have Pleistocene origins, with diversification times estimated to be younger than 1.5 Mya, in contrast to other Iberian species characterized by the persistence of generally much older lineages through glacial cycles , , which also seem to fit into the “refugia within refugia” model. This difference is simply a consequence of current taxonomic boundaries: older mitochondrial lineages of Iberolacerta do in fact exist, but they are nowadays associated to different, closely related species. In terms of the phylogeographic models of “S” (sanctuary) and “R” (refugia) species , the shallow mitochondrial diversification obtained from most clades of I. monticola (a truly, but relatively young “S” species, which apparently originated somewhere in this same region that it now inhabits, and shows different alleles that bear testimony of their ancestral diversity) is actually similar to the genetic signature of “R” species (taxa that colonized Iberia during the Quaternary, and lost a major part of their older lineages after extinction in all ancestral territories due to climate change).
Loss of Atlantic Forests and Habitat Fragmentation
In addition to the large effects of glaciations on the diversification of this species, the combined evidence from microsatellites and mitochondrial markers clearly shows that its current fragmented distribution at most nearby lowland populations has a very recent origin. All the species of Iberolacerta, except I. monticola, are confined to mountains in the centre and NE of the Iberian Peninsula, probably because of the low thermal quality and scarcity of refuges of lower elevation environments at those regions . In the NW, the observation of lowland populations associated to relict Atlantic forests of an otherwise montane species is not an exclusive characteristic of I. monticola –. Major woodland declines in NW Iberia occurred during the Galician-Roman Medieval Period , , often due to recurrent fires produced by past human societies to facilitate grazing . The loss of intervening suitable habitat, and the orientation of the retreating front of the Atlantic forests (from west to east), should have produced a succession of splits of the gene pools of I. monticola populations, which can be traced through the results of all our analyses of microsatellite variation, but particularly of FCA and Mantel tests. The significant association of Cavalli-Sforza chord distance (DC), but not FST-based indices, both with connectivity and with log-distance between populations, probably reflects the better performance of DC in recovering the topology of microsatellite trees , , notwithstanding the fact that most internal branches of the NJ tree for I. monticola populations have low statistical support. This still on-going process of fragmentation has produced a patchy distribution of I. monticola in the NW of the Iberian Peninsula, which includes large, moderate and small sized populations, and both montane and lowland habitats (OCCIDENTAL group).
Conflicting Phylogenetic Signals from Nuclear and Mitochondrial Markers at the Population of Serra da Estrela
Although mtDNA data suggest that the Estrela population is most closely related to other occidental populations (at Serra da Queixa and the Artabrian Gulf), thus implying that it has been separated from the CAMOR populations for nearly 1 million years, the microsatellite data do not support this conclusion, and indicate that it has been last connected with the populations of Courel and Ancares, at the western part of the Cantabrian Range, instead. Sex-biased gene flow is the most common explanation for such discordant patterns of biparental nuclear and maternal mitochondrial markers , but the evidence for higher male gene flow in I. monticola is so far not conclusive, and mostly based on differences in home-range sizes of the closely related species I. cyreni , . However, male-biased dispersal is a quite likely characteristic for most lizards with polyginous mating systems , such as I. monticola, so that it is probably a contributing factor to the phylogenetic pattern observed at Estrela. But there are other, not mutually excluding possibilities as well. One plausible scenario is that after the few hundred thousand years that followed the vicariance episodes, during which the different mitochondrial lineages of I. monticola evolved in isolation, there would have been a colonization of Serra da Estrela from northeastern populations (Courel-Ancares). A mitochondrial “occidental” allele may have drifted by chance to high frequency at the population of Estrela, even though the nuclear genomes bear the trace of that secondary contact. If the above scenario is correct then there may be alleles from the Cantabrian lineage III still present elsewhere in the Serra da Estrela.
Genetic Signatures of Isolation and Population Size Reduction
Small isolated populations of I. monticola show footprints of genetic erosion, such as a reduction of standing levels of genetic variation and, insofar as FST is accepted as a valid index of drift load , , a relative increase in the expected frequency of fixed deleterious mutations. Taking into account that endangered populations of other species generally display FST values exceeding 0.2 , , , then the conclusion that I. monticola is threatened by extinction in these isolated sites seems justified, particularly so if considering that there has been scarcely time for these populations to reach mutation-drift equilibrium, so that the observed FST value of 0.215 (twice the value obtained for “continuous” populations) is most likely to be an underestimate. However, there are other considerations that must be taken into account on this respect.
First, the frequency of segregating deleterious mutations and the mutation load of I. monticola at pre-fragmentation stages may have been much lower than for an undivided population. It all depends on whether the species is expected to largely fit a metapopulation model or not. In species displaying low natal and breeding dispersal, such as many lizards , , individuals are more likely to mate with those nearby, so that populations distributed over continuous habitats may actually be considered as large metapopulations, with fewer deleterious alleles and potentially a lower mutation load than an undivided population . Even for modest FST scores, such as those observed among “continuous” populations of I. monticola, the expected reduction in inbreeding depression and mutation load of the metapopulation as compared with an undivided population can be quite important , , thus being less prone to experience negative genetic effects upon fragmentation.
Second, small isolates of I. monticola show no evidence of overall excess of homozygotes, not even Lambre, a very small population that may have gone extinct by now , although inbreeding should be, in principle, much more intense in them than in large populations. This could be due, at least in part, to transient associative overdominance, produced either by local genetic linkage to the target loci of selection  or genomic effects on fitness . Besides, females may be choosing to mate with unrelated males in these reduced populations, or there may be overdispersion with respect to genetic similarity, similarly to what has been observed or suggested for other species after population declines in a variety of evolutionary contexts –.
The tempo and mode of the building-up of genetic differences among populations that ultimately become new species may assume endless forms . However, many species and species complexes in the Iberian Peninsula show concordant phylogeographic patterns, produced by the strong differentiation of populations that have survived in separate refugia throughout Pleistocene ice ages, aided by the high physiographic complexity and the wide range of climates of this part of the world . The persistence of these geographically congruent differentiated lineages in spite of potential gene flow, when cyclic range expansions presumably bring many of them repeatedly into contact, suggests the involvement of a general mechanism of speciation mediated by the evolution of intrinsic postzygotic isolating barriers . The test of this hypothesis should await for studies on the distribution of genotypes over a very small spatial scale at suture zones, complemented by fitness analyses of natural or experimental hybrids.
The Holocene may represent an inflexion point for the long-term survival of those genetic lineages more exposed to the anthropogenic perturbations of their habitats. Thus, successful heirs of many thousand years of evolution, with unique genetic characteristics forged in the engine of the cyclic climate changes of the Pleistocene, might not get through the next glacial stage, but become extinct relatively soon.
Bayesian phylogenetic tree of I. monticola populations based on mitochondrial sequences. The tree is rooted using I. cyreni as outgroup, and it includes representative sequences from I. martinezricai and I. galani. See legend of Figure 1B for instructions to read the statistical support of internal branches.
Different estimates of genetic variation at microsatellite loci, for the different geographical samples of I. monticola. (A) Expected heterozygosity in HW equilibrium (He); bars correspond to standard deviations. (B) Average allelic richness (blue bars) and private allelic richness (red bars), corrected for sample size.
Results of the analysis for genetic clustering using Structure. Colors correspond to the different clusters inferred by the analysis. The log likelihood of each assumed number of clusters (lnL) is shown, together with the % of independent runs that correspond to the represented partition of populations among clusters.
Identification of the most likely number of I. monticola populations by the analysis of microsatellite data with Structure v. 2.1. (A) Estimated log probability of data for the different number of inferred clusters (K); bars correspond to standard deviation, after 10 independent runs. (B) Rate of change in the log probability of data between successive k values (Δk). Both figures were obtained with the aid of Structure Harvester v. 0.56.4, http://taylor0.biology.ucla.edu/struct_harvest/.
Information about the populations and the genetic samples of I. monticola used in this work.
Information summary of the DNA markers used in this work.
This study is part of NR’s PhD thesis. Special thanks are given to Ricardo Ferreiro-Sanjurjo, who assisted in the field-work and in preparing samples for later use in the laboratory.
Conceived and designed the experiments: PG HN. Performed the experiments: PG OA NR. Analyzed the data: NR MV HN. Contributed reagents/materials/analysis tools: MV HN. Wrote the paper: HN. Collected samples in the field: PG OA. Processed the samples and carried out all the lab work: NR. Revised the manuscript: NR PG OA MV.
- 1. Raymo ME, Huybers P (2008) Unlocking the mysteries of the ice ages. Nature 451: 284–285.
- 2. Schmitt T (2009) Biogeographical and evolutionary importance of the European high mountain systems. Front Zool 6: 9.
- 3. Kropf M, Kadereit JW, Comes HP (2003) Differential cycles of range contraction and expansion in European high mountain plants during the Late Quaternary: insights from Pritzelago alpina (L.) O. Kuntze (Brassicaceae). Mol Ecol 12: 931–949.
- 4. Lande R (1998) Anthropogenic, ecological and genetic factors in extinction and conservation. Res Popul Ecol 40: 259–269.
- 5. Berec L, Angulo E, Courchamp F (2006) Multiple Allee effects and population management. Trends Ecol Evol 22: 185–191.
- 6. Fischer J, Lindenmayer DB (2007) Landscape modification and habitat fragmentation: a synthesis. Glob Ecol Biogeogr 16: 265–280.
- 7. Blomqvist D, Pauliny A, Larsson M, Flodin LA (2010) Trapped in the extinction vortex? Strong genetic effects in a declining vertebrate population. BMC Evol Biol 10: 33.
- 8. Lynch M, Conery J, Bürger R (1995) Mutation accumulation and the extinction of small populations. Am Nat 146: 489–518.
- 9. Mayer W, Arribas O (1996) Allozyme differentiation and relationship among the Iberian-Pyrenean mountain lizards. Herpetozoa 9: 57–61.
- 10. Arribas O, Carranza S, Odierna G (2006) Description of a new endemic species of mountain lizard from Northwestern Spain: Iberolacerta galani sp nov (Squamata: Lacertidae). Zootaxa 1240: 1–55.
- 11. Almeida AP, Rosa HD, Paulo OS, Crespo EG (2002) Genetic differentiation of populations of Iberian rock-lizards Iberolacerta (Iberolacerta) sensu Arribas (1999). J Zoolog Syst Evol Res 40: 57–64.
- 12. Carranza S, Arnold EN, Amat F (2004) DNA phylogeny of Lacerta (Iberolacerta) and other lacertine lizards (Reptilia: Lacertidae): did competition cause long-term mountain restriction? System Biodivers 2: 57–77.
- 13. Crochet PA, Chaline O, Surget-Groba Y, Debain C, Cheylan M (2004) Speciation in mountains: phylogeography and phylogeny of the rock lizards genus Iberolacerta (Reptilia: Lacertidae). Mol Phylogenet Evol 30: 860–866.
- 14. Mayer W, Arribas O (2003) Phylogenetic relationships of the European lacertid genera Archaeolacerta and Iberolacerta and their relationships to some other ‘Archaeolacertae’ (sensu lato) from Near East, derived from mitochondrial DNA sequences. J Zoolog Syst Evol Res 41: 157–161.
- 15. Pérez-Mellado V, Sá-Sousa P, Marquez R, Martínez-Solano I (2009) Iberolacerta monticola. IUCN Red List of Threatened Species. Version 2011.2 Available from: www.iucnredlist.org/.
- 16. Galán P, Vila M, Remón N, Naveira H (2007) Caracterización de las poblaciones de Iberolacerta monticola en el Noroeste ibérico mediante la combinación de datos morfológicos, ecológicos y genéticos. Munibe (Suplemento) 25: 34–43.
- 17. Galán P (1999) Declive y extinciones puntuales en poblaciones de baja altitud de Lacerta monticola cantabrica.. Bol Asoc Herpetol Esp 10: 47–51.
- 18. Galán P (2005) Herpetofauna de Galicia: situación actual y amenazas que inciden en su conservación. Recursos Rurais 2: 51–64.
- 19. Remón N, Galán P, Naveira H (2012) Chronicle of an extinction foretold: genetic properties of an extremely small population of Iberolacerta monticola.. Conserv Genet 13: 131–142.
- 20. Vidal-Romaní JR, Santos L (1994) La deglaciación finicuaternaria en el noroeste peninsular (Serra de Queixa-Invernadoiro, Ourense, Galicia): datos geomorfológicos y paleobotánicos. Cuaternario y Geomorfología 8: 33–44.
- 21. Fernández-Mosquera D, Marti K, Vidal-Romaní JR, Weigel A (2000) Late Pleistocene deglaciation chronology in the NW of the Iberian Peninsula using cosmic-ray produced 21Ne in quartz. Nucl Instrum Methods Phys Res B 172: 832–837.
- 22. Crowley TJ, North GR (1999) Paleoclimatology. New York: Oxford University Press.
- 23. Arribas O, Carranza S (2004) Morphological and genetic evidence of the full species status of Iberolacerta cyreni martinezricai (Arribas, 1996). Zootaxa 634: 1–24.
- 24. Remón N, Vila M, Galán P, Naveira H (2008) Isolation and characterization of polymorphic microsatellite markers in Iberolacerta monticola, and cross-species amplification in Iberolacerta galani and Zootoca vivipara.. Mol Ecol Resour 8: 1351–1353.
- 25. Park SDE (2001) Trypanotolerance in West African cattle and the population genetic effects of selection. PhD Dissertation. University of Dublin, Dublin, Ireland.
- 26. Rousset F (2008) GENEPOP’007: a complete re-implementation of the GENEPOP software for Windows and Linux. Mol Ecol Resour 8: 103–106.
- 27. Weir BS, Cockerham CC (1984) Estimating F-statistics for the analysis of population structure. Evolution 38: 1358–1370.
- 28. Goudet J (2001) FSTAT: a program to estimate and test gene diversities and fixation indices. Available from: www.unil.ch/izea/softwares/fstat.html.
- 29. Rice WR (1989) Analysing tables of statistical tests. Evolution 43: 223–225.
- 30. Piry S, Luikart G, Cornuet JM (1999) Bottleneck: A computer program for detecting recent reductions in the effective population size using allele frequency data. J Hered 90: 502–503.
- 31. Garza JC, Williamson EG (2001) Detection of reduction in population size using data from microsatellite loci. Mol Ecol 10: 305–318.
- 32. Campos JL, Posada D, Caballero A, Moran P (2007) Spatio-temporal genetic variability in sea trout (Salmo trutta) populations form north-western Spain. Freshw Biol 52: 510–524.
- 33. Bowcock AM, Ruiz-Linares A, Tomfohrde J, Minch E, Kidd JR, et al. (1994) High resolution of human evolutionary trees with polymorphic microsatellites. Nature 368: 455–457.
- 34. Goldstein DB, Ruiz Linares A, Cavalli-Sforza LL, Feldman MW (1995) An evaluation of genetic distances for use with microsatellite loci. Genetics 139: 463–471.
- 35. Dieringer D, Schlötterer C (2003) Microsatellite analyser (MSA): a platform independent analysis tool for large microsatellite data sets. Mol Ecol Notes 3: 167–169.
- 36. Felsenstein J (2005) PHYLIP: Phylogenetic Inference Package, Version 3.6. Available from: evolution.genetics.washington.edu/phylip.html.
- 37. Tamura K, Dudley J, Nei M, Kumar S (2007) MEGA4: Molecular Evolutionary Genetics Analysis (MEGA) software version 4.0. Mol Biol Evol 24: 1596–1599.
- 38. Belkhir K, Borsa P, Chikhi L, Raufaste N, Bonhomme F (2004) GENETIX 4.05, logiciel sous Windows TM pour la génétique des populations. Available from: www.genetix.univ-montp2.fr/genetix/genetix.htm.
- 39. Takezaki N, Nei M (1996) Genetic distances and reconstruction of phylogenetic trees from microsatellite DNA. Genetics 144: 389–399.
- 40. Pritchard JK, Stephens M, Donnelly P (2000) Inference of population structure using multilocus genotype data. Genetics 155: 945–959.
- 41. Evanno G, Regnaut S, Goudet J (2005) Detecting the number of clusters of individuals using the software STRUCTURE: a simulation study. Mol Ecol 14: 2611–2620.
- 42. Rosenberg NA (2004) DISTRUCT: a program for the graphical display of population structure. Mol Ecol Notes 4: 137–138.
- 43. Farris JS, Kallersjo M, Kluge AG, Bult C (1994) Testing significance of incongruence. Cladistics 10: 315–319.
- 44. Mickevich MF, Farris JS (1981) The implications of congruence in Menidia.. Syst Zool 30: 351–370.
- 45. Swofford DL (1998) PAUP*: Phylogenetic Analysis Using Parsimony (*and Other Methods), Version 4. Sunderland: Sinauer Associates.
- 46. Tamura K, Peterson D, Peterson N, Stecher G, Nei M, et al. (2011) MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods. Mol Biol Evol 28: 2731–2739.
- 47. Gu X, Zhang J (1997) A simple method for estimating the parameter of substitution rate variation among sites. Mol Biol Evol 14: 1106–1113.
- 48. Helaers R, Milinkovitch MC (2010) MetaPIGA v2.0: maximum likelihood large phylogeny estimation using the metapopulation genetic algorithm and other stochastic heuristics. BMC Bioinformatics 11: 379.
- 49. Posada D (2008) jModelTest: Phylogenetic model averaging. Mol Biol Evol 25: 1253–1256.
- 50. Huelsenbeck JP, Ronquist F (2001) MrBayes: Bayesian inference of phylogeny. Bioinformatics 17: 754–755.
- 51. Ronquist F, Huelsenbeck JP (2003) MrBayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics 19: 1572–1574.
- 52. Kass RE, Raftery AE (1995) Bayes factors. J Am Stat Assoc 90: 773–795.
- 53. Arnold EN, Arribas O, Carranza S (2007) Systematics of the Palaearctic and Oriental lizard tribe Lacertini (Squamata : Lacertidae : Lacertinae), with descriptions of eight new genera. Zootaxa 1430: 1–86.
- 54. Hipsley CA, Himmelmann L, Metzler D, Müller J (2009) Integration of Bayesian molecular clock methods and fossil-based soft bounds reveals early Cenozoic origin of African lacertid lizards. BMC Evol Biol 9: 151.
- 55. Rambaut A (2009) FigTree. Tree Figure Drawing Tool. Available from: http://tree.bio.ed.ac.uk/.
- 56. Posada D, Crandall KA (2001) Intraspecific gene genealogies: trees grafting into networks. Trends Ecol Evol 16: 37–45.
- 57. Clement M, Posada D, Crandall KA (2000) TCS: a computer program to estimate gene genealogies. Mol Ecol 9: 1657–1659.
- 58. Glez-Peña D, Gómez-Blanco D, Reboiro-Jato M, Fdez-Riverola F, Posada D (2010) ALTER: program-oriented conversion of DNA and protein alignments. Nucleic Acids Res 38: W14–W18.
- 59. Cavalli-Sforza LL, Edwards AWF (1967) Phylogenetic analysis models and estimation procedures. Am J Hum Genet 19: 233–257.
- 60. Excoffier L, Smouse PE, Quattro JM (1992) Analysis of molecular variance inferred from metric distances among DNA haplotypes: application to human mitochondrial DNA restriction data. Genetics 131: 479–491.
- 61. Mantel N (1967) The detection of disease clustering and a generalized regression approach. Cancer Res 27: 209–220.
- 62. Jensen JL, Bohonak AJ, Kelley ST (2005) Isolation by distance, web service. BMC Genet 6: 13.
- 63. Rousset F (1997) Genetic differentiation and estimation of gene flow from F-statistics under isolation by distance. Genetics 145: 1219–1228.
- 64. Rowe G, Beebee TJC, Burke T (2000) A microsatellite analysis of natterjack toad, Bufo calamita, metapopulations. Oikos 88: 641–651.
- 65. Lee-Yaw JA, Davidson A, McRae BH, Green DM (2009) Do landscape processes predict phylogeographic patterns in the wood frog? Mol Ecol 18: 1863–1874.
- 66. Ersts PJ (2007) Geographic Distance Matrix Generator, Version 1.2.3. Available from: biodiversityinformatics.amnh.org/open_source/gdmg.
- 67. Excoffier L, Lischer HEL (2010) Arlequin suite ver 3.5: A new series of programs to perform population genetics analyses under Linux and Windows. Mol Ecol Resour 10: 564–567.
- 68. Gómez A, Lunt DH (2007) Refugia within refugia: patterns of phylogeographic concordance in the Iberian Peninsula. In: Weiss S, Ferrand N, editors. Phylogeography of southern European refugia: Evolutionary perspectives on the origins and conservation of European biodiversity. Dordrecht: Springer. 155–188.
- 69. Recuero E, García-París M (2011) Evolutionary history of Lissotriton helveticus: multilocus assessment of ancestral vs. recent colonization of the Iberian Peninsula. Mol Phylogenet Evol 60: 170–182.
- 70. Mouret V, Guillaumet A, Cheylan M, Pottier G, Ferchaud AL, et al. (2011) The legacy of ice ages in mountain species: post-glacial colonization of mountain tops rather than current range fragmentation determines mitochondrial genetic diversity in an endemic Pyrenean rock lizard. J Biogeogr 38: 1717–1731.
- 71. Arribas O, Odierna G (2004) Karyological and osteological data supporting the specific status of Iberolacerta (cyreni) martinezricai (Arribas, 1996). Amphib-reptil 25: 359–367.
- 72. Coope GR, Wilkins AS (1994) The response of insect faunas to glacial-interglacial climatic fluctuations. Philos Trans R Soc Lond B Biol Sci 344: 19–26.
- 73. Hewitt GM (2000) The genetic legacy of the Quaternary ice ages. Nature 405: 907–913.
- 74. Schmitt T (2007) Molecular biogeography of Europe: Pleistocene cycles and postglacial trends. Front Zool 4: 11.
- 75. Rodríguez T, Trigo D, Cosín D (1997) Biogeographical zonation of the western Iberian peninsula on the basis of the distribution of earthworm species. J Biogeogr 24: 893–901.
- 76. Deffontaine V, Libois R, Kotlík P, Sommer R, Nieberding C, et al. (2005) Beyond the Mediterranean peninsulas: evidence of central European glacial refugia for a temperate forest mammal species, the bank vole (Clethrionomys glareolus). Mol Ecol 14: 1727–1739.
- 77. Hewitt GM (2004) The structure of biodiversity–insights from molecular phylogeography. Front Zool 1: 1–16.
- 78. Augustin L, Barbante C, Barnes PR, Barnola JM, Bigler M, et al. (2004) Eight glacial cycles from an Antarctic ice core. Nature 429: 623–628.
- 79. Hewitt GM (1996) Some genetic consequences of ice ages, and their role in divergence and speciation. Biol J Linn Soc Lond 58: 247–276.
- 80. Bazin E, Glémin S, Galtier N (2006) Population size does not influence mitochondrial genetic diversity in animals. Science 312: 570–571.
- 81. Galtier N, Nabholz B, Glémin S, Hurst GDD (2009) Mitochondrial DNA as a marker of molecular diversity: a reappraisal. Mol Ecol 18: 4541–4550.
- 82. Arnold EN (1981) Competition, evolutionary change and montane distributions. In: Forey PL, Greenwood PH, editors. The Evolving Biosphere: Chance, Change and Challenge. London: Cambridge University Press. 217–228.
- 83. Godinho R, Mendonça B, Crespo EG, Ferrand N (2006) Genealogy of the nuclear beta-fibrinogen locus in a highly structured lizard species: comparison with mtDNA and evidence for intragenic recombination in the hybrid zone. Heredity 96: 454–463.
- 84. Godinho R, Crespo EG, Ferrand N (2008) The limits of mtDNA phylogeography: complex patterns of population fragmentation, expansion and admixture in the highly structured Iberian lizard Lacerta schreiberi are only revealed by the use of nuclear markers. Mol Ecol 17: 4670–4683.
- 85. Martínez-Solano I, Teixeira J, Buckley D, García-París M (2006) Mitochondrial DNA phylogeography of Lissotriton boscai (Caudata, Salamandridae): evidence for old, multiple refugia in an Iberian endemic. Mol Ecol 15: 3375–3388.
- 86. Fitze P, Gonzalez-Jimena V, San-Jose L, San Mauro D, Aragon P, et al. (2011) Integrative analyses of speciation and divergence in Psammodromus hispanicus (Squamata: Lacertidae). BMC Evol Biol 11: 347.
- 87. Monasterio C, Salvador A, Iraeta P, Díaz JA (2009) The effects of thermal biology and refuge availability on the restricted distribution of an alpine lizard. J Biogeogr 36: 1673–1684.
- 88. Baselga A, Novoa F (2008) Coleoptera in a relict forest of Spain: Implications of hyperdiverse taxa for conservation strategies. Ann Entomol Soc Am 101: 402–410.
- 89. Pino-Pérez JJ, Martínez-Fernández A, Camaño-Portela JL, Pino-Pérez R (2009) Nueva cita de Endromis versicolora (Linnaeus, 1758) (Lepidoptera, Endromidae) para Galicia (NO España). Boletín BIGA 6: 125–127.
- 90. Martínez-Fernández A, Pino-Pérez R, Camaño-Portela JL, PIno-Pérez JJ (2008) Nuevas citas de Aglia tau (Linnaeus, 1758) (Lepidoptera: Saturniidae, Agliinae) para Galicia (NO España). Boletín BIGA 4: 87–89.
- 91. Galán P, Ludewig AK, Kmiec J, Hauswaldt S, Cabana M, et al. (2010) Low mitochondrial divergence of rediscovered southern relict populations of Rana temporaria parvipalmata in Spain. Amphib-reptil 31: 144–148.
- 92. Galán P (2000) Primeros datos sobre el murciélago bigotudo Myotis mystacina (Kuhl, 1817) en Galicia. Galemys 12: 41–47.
- 93. Muñoz-Sobrino C, Ramil-Rego P, Gómez-Orellana L, Díaz-Varela RA (2005) Palynological data on major Holocene climatic events in NW Iberia. Boreas 34: 381–400.
- 94. Muñoz-Sobrino C, Ramil-Rego P, Gómez-Orellana L (2007) Late Würm and early Holocene in the mountains of northwest Iberia: biostratigraphy, chronology and tree colonization. Veg Hist Archaeobot 16: 223–240.
- 95. Carrión J, Kaal J, López-Sáez JA, López-Merino L, Martínez-Cortizas A (2010) Holocene vegetation changes in NW Iberia revealed by anthracological and palynological records from a colluvial soil. The Holocene 20: 53–66.
- 96. Toews DP, Brelsford A (2012) The biogeography of mitochondrial and nuclear discordance in animals. Mol Ecol 21: 3907–3930.
- 97. Aragón P, López P, Martín J (2001) Seasonal changes in activity and spatial and social relationships of the Iberian rock lizard, Lacerta monticola.. Can J Zool 79: 1965–1971.
- 98. Aragón P, López P, Martín J (2004) The ontogeny of spatio-temporal tactics and social relationships of adult male Iberian rock lizards, Lacerta monticola.. Ethology 110: 1001–1019.
- 99. Johansson H, Surget-Groba Y, Thorpe RS (2008) Microsatellite data show evidence for male-biased dispersal in the Caribbean lizard Anolis roquet.. Mol Ecol 17: 4425–4432.
- 100. Keller LF, Waller DM (2002) Inbreeding effects in wild populations. Trends Ecol Evol 17: 230–241.
- 101. Jaquiéry J, Guillaume F, Perrin N (2009) Predicting the deleterious effects of mutation load in fragmented populations. Conserv Biol 23: 207–218.
- 102. Kawamura K, Kubota M, Furukawa M, Harada Y (2007) The genetic structure of endangered indigenous populations of the amago salmon, Oncorhynchus masou ishikawae, in Japan. Conserv Genet 8: 1163–1176.
- 103. Eckstein RL, O’neill RA, Danihelka J, Otte A, Köhler W (2006) Genetic structure among and within peripheral and central populations of three endangered floodplain violets. Mol Ecol 15: 2367–2379.
- 104. Olsson M, Shine R (2003) Female-biased natal and breeding dispersal in an alpine lizard, Niveoscincus microlepidotus.. Biol J Linn Soc Lond 79: 277–283.
- 105. Waldman B, McKinnon JS (1993) Inbreeding and outbreeding in fishes, amphibians, and reptiles. In: Thornhill NW, editors. The Natural History of Inbreeding and Outbreeding: Theoretical and Empirical Perspectives. Chicago: The University of Chicago Press. 250–282.
- 106. Whitlock MC (2002) Selection, load and inbreeding depression in a large metapopulation. Genetics 160: 1191–1202.
- 107. Theodorou K, Couvet D (2006) Genetic load in subdivided populations: interactions between the migration rate, the size and the number of subpopulations. Heredity 96: 69–78.
- 108. Glémin S, Ronfort J, Bataillon T (2003) Patterns of inbreeding depression and architecture of the load in subdivided populations. Genetics 165: 2193–2212.
- 109. Balloux F, Amos W, Coulson T (2004) Does heterozygosity estimate inbreeding in real populations? Mol Ecol 13: 3021–3031.
- 110. Coltman DW, Slate J (2003) Microsatellite measures of inbreeding: a meta-analysis. Evolution 57: 971–983.
- 111. Boudjemadi K, Lecomte J, Clobert J (1999) Influence of connectivity on demography and dispersal in two contrasting habitats: an experimental approach. J Anim Ecol 68: 1207–1224.
- 112. Bowler DE, Benton TG (2005) Causes and consequences of animal dispersal strategies: relating individual behaviour to spatial dynamics. Biol Rev 80: 205–225.
- 113. Clobert J, Le Galliard JF, Cote J, Meylan S, Massot M (2009) Informed dispersal, heterogeneity in animal dispersal syndromes and the dynamics of spatially structured populations. Ecol Lett 12: 197–209.
- 114. Zamudio KR, Sinervo B (2003) Ecological and social contexts for the evolution of alternative mating strategies. In: Fox SF, McCoy JK, Baird TA, editors. Lizard Social Behavior. Baltimore: The Johns Hopkins University Press. 83–106.
- 115. Hoffman JI, Forcada J, Trathan PN, Amos W (2007) Female fur seals show active choice for males that are heterozygous and unrelated. Nature 445: 912–914.
- 116. Sinervo B, Clobert J (2003) Morphs, dispersal behavior, genetic similarity, and the evolution of cooperation. Science 300: 1949–1951.
- 117. Howard DJ, Berlocher SH (1998) Endless forms: species and speciation. New York: Oxford University Press.
- 118. Forsdyke D (2001) The origin of species, revisited: a Victorian who anticipated modern developments in Darwin’s theory. Montreal: McGill Queens University Press.