The study of the European plethodontid salamander Hydromantes strinatii using allozyme and mitochondrial markers showed a strong geographical genetic structure. This was likely the outcome of different evolutionary mechanisms leaving their signature despite the effects of the genetic drift due to the low population size typical of this species. Two highly divergent clades were identified in the eastern and central-western part of the range, with further geographic sub-structure. Nuclear and mitochondrial markers substantially recovered the same population groups but were conflicting in reconstructing their relationships. This apparent incongruence highlighted the action of different mechanisms such as secondary contacts and incomplete lineage sorting in originating the observed genetic variation. The troglophilic habit of this species provided the opportunity to show the importance of caves as local refugia in maintaining the genetic diversity through the persistence of local populations. Accordingly, high nucleotide and haplotype diversity, strong geographic genetic structuring and lack of expansion were evidenced. This signature was found in the populations from the Ligurian and Maritime Alps, in agreement with the complex orography and paleoclimatic history of this Mediterranean hotspot.
Citation: Cimmaruta R, Lucente D, Nascetti G (2015) Persistence, Isolation and Diversification of a Naturally Fragmented Species in Local Refugia: The Case of Hydromantes strinatii. PLoS ONE 10(6): e0131298. https://doi.org/10.1371/journal.pone.0131298
Editor: Gyaneshwer Chaubey, Estonian Biocentre, ESTONIA
Received: November 3, 2014; Accepted: June 1, 2015; Published: June 24, 2015
Copyright: © 2015 Cimmaruta 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
Data Availability: All relevant data are available within the paper and its Supporting Information files.
Funding: The authors have no support or funding to report.
Competing interests: Roberta Cimmaruta is an Academic Editor of PLOS ONE. Nonetheless, this does not alter the authors' adherence to all the PLOS ONE policies on sharing data and materials.
Cave species are considered particularly fragile and endangered due to their strict ecological requirements, making them poorly able to face climatic variation. Also, their strong association with underground retreats constrains their populations to low size and poor genetic diversity . However, some recent data started to overturn this view, especially for troglophilic animals that are able to exploit both subterranean and epigean habitats. These features could make troglophilic species more resistant to climate changes than surface species since they have the possibility to draw back into local retreats under unfavourable external conditions and wait for better climate while sheltered. This hypothesis has been fuelled by recent case studies showing similar patterns of persistence in isolated troglophilic species  but also in surface species linked to patchy and heterogeneous habitats, thus pointing out the relevance of localized refugia in warranting the persistence of species through time [3–5]. High genetic diversity coupled with high genetic structuring, minimal population expansion and the persistence of local populations even in the presence of unfavourable Pleistocenic climatic conditions, are among the features observed. This finding has fostered the idea that localized refugia may have had an important role, besides the well known role played by macrorefugia, in assisting species persistence and diversification through Plio-Pleistocenic climate changes, especially in areas affected by deep changes but left free from ice cover [6–9].
The European plethodontid salamanders genus Hydromantes are perfect candidates for these kind of studies. Their biological and ecological features would suggest species fragility: Hydromantes are lungless thus rely on cutaneous respiration and need steady moist and fresh environments to avoid dehydration and respiratory insufficiency. Moreover these species lack an aquatic larval stage since the metamorphosis is completed within the egg, requiring moist, fresh and steady habitats where females can attend to their eggs until hatching occurs [10–13]. For these reasons there is a strong association of Hydromantes with underground retreats, such as caves and fissure systems, that are able to warrant the environmental conditions they need during unfavourable climatic periods such as Mediterranean summer. At the same time, European Hydromantes are generally characterized by old lineages and high genetic variation suggesting persistent and stable populations despite their very small size [10,14–16].
With the aim of explaining the apparently contrasting features of European plethodontids in the light of historical climate changes and localized retreats, we analyzed the genetic structure and phylogeography of H. strinatii. Among the eight species of Hydromantes [17,18], H. strinatii is particularly suited for this type of study since the central and western part of its range is in the Ligurian and Maritime Alps, between Italy and southern France. This area is characterized by a very complex orography, including karst areas, and by a peculiar paleoclimatic history. The ice sheet covering the Western Alps during Quaternary glaciations showed a patchy distribution in the coastal zones and many peripheral areas remained free from ice. These refugial micro-areas now host a strikingly high species richness and endemism concentration of plant species [19–21] and constitute a zone of coexistence of in situ differentiated lineages in animals [22–24].
In this work, we used partial sequences of the mitochondrial genes cytochrome-b (cytb) and NADH-dehydrogenase sub-unit 2 (ND2) and allozyme analysis to study the genetic structure and the phylogeography of H. strinatii. This allowed for the disentangling of the different evolutionary processes leading to the extant pattern of diversification in H. strinatii. We verified whether persistence in localized refugia contributed to the present genetic diversity of the species leaving the expected signature of high haplotypic and nucleotidic diversity associated to strong geographic structuring and lack of expansion. Finally, we tried to assess whether the distinctive topography and paleoclimatic history of the Ligurian and Maritime Alps was relevant in determining patterns and processes acting on H. strinatii by comparing the pattern of genetic diversity observed in the populations from this central-western part of the range vs. those observed in the easternmost populations, living in a more homogeneous environment.
Materials and Methods
The specimens of H. strinatii we studied belong to the collection of the Zoological Museum “La Specola” of the University of Florence (Italy) and were kindly provided by prof. Benedetto Lanza. Some specimens from a few localities were sampled on purpose under the licenses required by the corresponding authorities.
The permits of collecting, mark, collect tissues and release specimens was given by the Italian Ministry of the Environment (protocols DPN2009/0026530 and 0042634PNM07/08/13) according to the law DPR 357/97. The permits broadly allowed the collection of biological tissues without mentioning any protocol to be followed. No approval of ethics committee was required by both the Italian law and the EU directives on the use of animals for scientific purposes in force during the study period (Legislative Decree 116/92 and EU Directive 609/86).
For tissue sampling salamanders were captured manually and a small piece of about 2–3 mm was cut from the tail tip after keeping the tail on an instant-ice pack for about one minute. No anaesthetics were used to avoid possible mortality due to the high sensitivity of Hydromantes skin. Tissue samples were immediately frozen in a portable liquid nitrogen storable tank and sampled individuals were then released. No individuals were brought to the laboratory or sacrificed.
Sampling and laboratory procedures
An overall number of 385 specimens of H. strinatii were analysed from 30 sites distributed throughout the species range (Table 1, Fig 1). Standard horizontal starch gel electrophoresis was carried out for all samples using 33 putative allozyme loci (S1 Table) and using the laboratory procedures described in detail in .
Colours denote the seven sub-clades recovered by phylogenetic analyses, with the exception of black populations that were included in allozyme analysis only.
Total genomic DNA was extracted from the frozen tissue of 194 individuals using the cetyltrimethylammonium bromide (CTAB) protocol .
Partial sequences of the mitochondrial genes cytochrome-b (cytb) and NADH dehydrogenase subunit 2 (ND2) were obtained using specifically designed primers: HST-1f (5’-TTTATTGATTTACCAACCCCATCT-3’) and DEB-1r (5’-CAGGGGTGAAGTTTTCTGGAT-3’) for cytb; HND1-f (5’-TCAAGCTTATCCACCGGAAC-3’) and MAT2-r (5’-TTGGTGGTAGTCCGCCTAAG-3’) for ND2. Amplification was performed by polymerase chain reaction (PCR) in a volume of 25 μl containing MgCl2 (2.5 mM), the reaction buffer (1X; Promega), the four dNTPs (0.2 mM each), the two primers (0.2 μM each), the enzyme Taq polymerase (2 U; Promega) and 2 μl of DNA template. PCR reactions were carried out in a Hain Lifescience Q-Sat 24 thermal cycler using the following program: denaturation at 94°C for 5 minutes followed by 35 cycles at 94°C for 30 s, 53°C for 1 min, 72°C for 1 min and a final elongation step at 72°C for 10 min.
Purification and sequencing reactions were outsourced to Macrogen Inc. (www.macrogen.com).
Electropherograms were independently checked by eye by two of the Authors using Chromas v.1.6 (Technelysium Pty Ltd) and sequences were then aligned using the software ClustalX v.1.83 .
Mitochondrial data analysis
In order to reconstruct the phylogenetic relationships between mitochondrial lineages, we conducted maximum likelihood (ML) and Bayesian inference (BI) analyses for the combined dataset of cytb and ND2 genes, and applying a partition strategy by genes in both cases. Sequences of both cytb and ND2 genes were obtained from Sardinian species H. supramontis and H. imperialis and were used as outgroups (GenBank accession n. KJ834013-14 and KJ834057-58)
We computed ML analysis in RAxML GUI v.1.3  using a GTRGAMMA model and setting partitions by gene. The ‘ML + thorough bootstrap’ option, with one thousand bootstrap replicates and ten independent searches was implemented and a 50% majority-rule consensus tree was computed. Bayesian inference was carried out using MrBayes v.3.2.2  and specifying different evolutionary models for each gene. When the outgroup was excluded, the following optimal models of sequence evolution were selected with jModelTest v.2.1.2  under a Bayesian Information Criterion (BIC) and starting with a ML optimized tree: TIM3+I for the cytb gene and TrN+I for the ND2 gene. We ran three ‘heated’ and one ‘cold’ chain for 2 million generations, and sampled every 100 generations discarding 25% of the total sampled trees from the beginning of the chain as burn-in. Standard deviations of split frequencies among chains resulted in less than 0.01, and potential scales reduction factors (PSRF) for all parameters were close to one indicating that convergence was reached. We used Tracer v1.6.0 to check for an acceptable number of independent samples .
The distance-based least squares (LS) method  implemented in DAMBE 5.3.109  was used to estimate the Time to the Most Recent Common Ancestor (TMRCA) after determining that the evolutionary rate was constant through a likelihood ratio test. The analysis was carried out on the topology of the Bayesian tree for the concatenated data set using the ‘MLCompositeTN93’ genetic distance. According to the literature, all the Authors agree in dating back the split between eastern Sardinian and mainland Hydromantes lineages to the Messinian salinity crisis regardless of the markers used in their studies [15,17]. Therefore, the analyses were conducted by constraining the split node between mainland Hydromantes species (represented by H. strinatii) and Eastern Sardinian species (represented by H. supramontis and H. imperialis) at 5.33 ma, which is the end of the Messinian salinity crisis (5.96–5.33 ma) [33,34]. The standard deviation of the time estimates was calculated by bootstrap re-sampling with 1000 pseudoreplicates. Construction of a haplotype network was carried out by a median-joining (MJ) algorithm  as implemented in the software Network v.188.8.131.52 (http://www.fluxus-engineering.com) under Greedy FHP criterion  and default parameter values. Genetic distances between the haplo-groups identified were computed in MEGA  under the Kimura two-parameter model (K2P) .
Population genetic structure and demographic analysis.
To investigate population genetic structure, we first ran our data in SAMOVA v.1.0 (Spatial Analysis of Molecular Variance; ) testing K values from 2 to 20 by performing 100 simulated annealing processes. Additionally, we carried out the identification of groups under a Bayesian clusterization approach using the software BAPS v.6.0 [40–42]. We implemented a genetic mixture analyses using the non spatial clustering option and ran five replicates for each K ranging between 2 to 20.
Once the best number of groups was selected according to both SAMOVA and BAPS, all the subsequent analyses were carried out on each detected population group.
Haplotype (h) and nucleotide (π) diversity as well as the gene flow parameter Nm were estimated for each cluster using DNAsp v5.10 .
Tajima’s D , Fu’s Fs  and Ramos-Onsins & Rozas’ R2  statistical neutrality tests were applied to each group to detect possible historical population growth. Also, we examined the distribution of the number of differences between pairs of haplotypes by a mismatch analysis  and evaluating both the sum of square deviations (SSD)  and Harpending’s raggedness index (RI)  for each group. Tajima’s D, Fu’s Fs, and the mismatch distribution were computed in Arlequin v.3.5 , while we used DNAsp v.5 for R2 computations .
To verify if the population genetic structure conformed to an isolation by distance model (IBD), a Mantel test was executed in Arlequin v.3.5 . A genetic Fst distance matrix was performed against a geographic distance matrix (with distances expressed in km) using 10000 permutations. Computations were done for each single group and for the whole population set.
Allozyme data analysis
Allozyme allele frequencies, conformity to Hardy-Weinberg equilibrium and linkage-disequilibria were calculated using the software Genepop 4.2  and testing for departures from expectations using Fisher’s method. The parameters of genetic variability per population were estimated using the software Genetix : mean number of alleles (Na), observed heterozygosity (Ho), expected heterozygosisty (He), percentage of polymorphic loci under 99% criterion (P99). The softwares Genodive 2.0  and FSTAT 184.108.40.206  were used to estimate the effective number of alleles (NE) and the allelic richness (AR), respectively.
The partitioning of genetic diversity was analyzed for variable loci using the Fixation index Fst as implemented in Genepop 4.2 . The significance of pairwise Fst values was tested using Fisher’s method followed by Bonferroni correction .
A Principal Component Analysis was carried out based on a matrix of covariance of allele frequencies as implemented in Genodive 2.0 , and the significance of the population differentiation represented by the PCA-axes was tested by 100000 permutations.
The identification of population groups was obtained using BAPS v.6.0 [40,57], setting the non-spatial clustering option and running 5 replicates for each K value between 2 and 20. Also, a Bayesian model-based algorithm was used to assign individuals to genetically homogeneous groups, as implemented in STRUCTURE v.2.3.4 . We used an admixture ancestry model assuming correlated allele frequencies and different values of Fst for different subpopulations due to the high levels of natural fragmentation of Hydromantes populations. Priors were set choosing sampling location information (LOCPRIOR) and using both the mean value of Fst and the associated standard deviation obtained by previous calculations. Length of the burn-in period was of 100000 replicates followed by 100000 Markov chains Monte Carlo (MCMC) replicates, and fifteen runs were conducted for each K ranging from 2 to 12. The Evanno algorithm , as implemented in Structure Harvester v.0.6.94 , was used to select the optimal K based on both the log probability of the data and the inferred ∆K. The independent runs relative to the optimal K value were aligned with CLUMPP v.1.1.2  under the Greedy algorithm. The results were graphically displayed by DISTRUCT v.1.1 .
An analysis of molecular variance was carried out assuming a stepwise model as implemented in Genodive 2.0  and partitioning populations according to the K = 5 groups recovered by STRUCTURE.
A Mantel test was performed in Arlequin v.3.5  contrasting a Fst distance matrix vs. a geographic distance matrix (km). The IBD hypothesis was tested for the whole population set, for the two main mitochondrial clades and for the K groups recovered by STRUCTURE.
Mitochondrial data analysis
The 687-bp fragment of cyt-b sequenced had 59 variable positions (5 singletons) 54 of which were parsimony informative, and provided 24 different haplotypes over the 194 specimens scored. The obtained sequences have been deposited in GenBank (Accession n: KJ834015-38). Nucleotide percentages were: T 33.9%, C 22.0%, A 30.4%, and G 13.7%. The estimated nucleotide diversity (π) had a mean value of 0.028.
The 702 bp fragment from ND2 gene had 54 variable positions (1 singleton), 53 of which were parsimony informative. The 194 specimens scored provided 18 haplotypes, available in GenBank (Accession n: KJ834039-56). Nucleotide percentages were: T 31.2%, C 23.2%, A 35.6% and G 10.0%. The estimated nucleotide diversity (π) had a mean value of 0.025.
The alignment of the concatenated sequences was of 1389 bp, and provided an overall number of 30 haplotypes, as listed in Table 1. The estimated values of nucleotide (π) and haplotype (h) diversity were 0.026 and 0.87, respectively. The genetic divergence calculated according to Kimura 2 Parameter (K2P) was 0.028 (±0.003).
Each haplotype was recovered in a single or a few geographically very close localities (Table 1).
All the phylogenetic reconstructions agreed in showing two well supported reciprocally monophyletic groups, including the haplotypes recovered in the eastern and western part of the range, respectively: the eastern clade (Clade A) included the haplotypes recovered from samples 1 to 21 and the western clade (Clade B) contained those from samples 22 to 30 (Fig 2). These two clades received a high support for both ML and BI analyses (Fig 2). Clade A was further subdivided into four geographically distinct sub-clades including the haplotypes from: the easternmost part of the range (sub-clade A1, samples 1–11), the “Rapallo area” (sub-clade A2, samples 12–14), the “Finalese” region (sub-clade A3, samples 15–18), and the “Roburent” region (sub-clade A4, samples 19–21). Clade B was subdivided into three sub-clades each including the haplotypes from a geographic area: “San Bartolomeo Hills” (B1, samples 22–24), “Tenarda” area in the Ligurian Alps (B2, sample 25), and the French Maritime Alps (B3, samples 26–30). The outcome of the median-joining network calculation provided further support for the results of the tree-building methods. We recovered the same two main phylogroups (A and B) separated from a total of 62 steps (Fig 3). Within each phylogroup, the haplotypes were structured in seven geographically distinct haplogroups connected by 7 to 17 mutational steps and completely congruent with the seven sub-clades recovered in the tree-based analyses. Sub-clade A1 displayed a star-like pattern, with the haplotype hst1 found at a high frequency in all the samples and representing 91.5% of its haplotypic diversity. In the sub-clade B3, by grouping the haplotypes from the French Maritime Alps, each population was characterized by its own exclusive haplotype(s), and the haplotypes recovered from Tenda (STN, 26) showed an intermediate position between the sub-clade B2 (Tenarda, STE, sample 25) and the other haplotypes from the French Maritime Alps (Fig 3).
The tree shows the results for Bayesian Inference (BI) and Maximum Likelihood (ML) analyses. Posterior probability and bootstrap values are reported on each tree node. Both phylogenetic reconstructions showed the occurrence of two main clades A and B, subdivided respectively into four (A1, A2, A3, A4) and three (B1, B2, B3) sub-clades.
The size of the circles is proportional to the frequency of each haplotype. Haplotypes are connected by distances proportional to mutational steps with the small grey circles representing missing haplotypes. The seven haplogroups are congruent to the seven sub-clades recovered by phylogenetic analysis; the two main clades A and B are separated by 62 mutational steps.
The estimates of K2P distance between the seven lineages gave values comprised between 0.8% and 5.4%. The minimum divergence of 0.8% (p-distance = 0.8%) was recovered between the sub-clades A2 and A3. The values of maximum divergence comprised between 5.0% and 5.4% (p-distance values from 4.7% to 5.2%) were always found in pairwise comparisons between sub- clades A vs. B.
Population genetic structure and demographic history.
The SAMOVA analysis showed that the best partitioning of genetic variation was achieved with seven clusters: Fct index grew from 0.79 to 0.95 for K between 2 and 7 and then slightly moved between 0.96 and 0.99 for K between 7 and 25 (S1 File). Accordingly, the algorithm implemented in BAPS recovered 7 as the best group membership solution with a posterior probability of 1.00 (S1 File). The 7 population groups inferred were completely coincident with the seven sub-clades recovered with the phylogenetic analyses, confirming the genetic and geographic pattern of differentiation previously shown. The AMOVA analysis was performed on the seven groups recovered by SAMOVA and showed that nearly all the genetic variation was due to the among-group level of variation (95.23%, p < 0.0001), while 3.78% was due to the among-population within-group level and 1.00% to the within-population level (Table 2).
The seven clades had heterogeneous levels of both haplotype and nucleotide diversity with lower values presented by the easternmost sub-clades (A1, A2; π spanning 0.00004 to 0.00012; h ranging between 0.063 and 0.163) and the highest values recorded for the French Maritime Alps clade (B3) with π = 0.00472 and h = 0.846.
Inferred levels of gene flow were very low both between groups (average Nm = 0.02) and within groups (Nm = 0.04–1.93) with the lowest values recorded within sub-clades A4 and B3.
The Mantel test results showed no correlation between genetic and geographic distances within the seven groups detected. However, a pattern of IBD came out when considering the entire species range (r = 0.52; p < 0.0001). A significant correlation was also observed within clade A (r = 0.71; p < 0.0001), while clade B exhibited no IBD (r = 0.22; p < 0.11).
The demographic test statistics and the analysis of the mismatch distribution computed for each of the seven clades showed only weak signs of past demographic expansion (Table 3). Both Tajima’s D and Fu’s Fs gave negative and significant values for the eastern clade A1 and for the S. Bartolomeo clade B1. However, the most sensitive R2 test did not result in any significant value. On the contrary, the mismatch distribution showed that the frequencies of pairwise haplotype differences expected under the assumption of a sudden demographic expansion and those observed from the data were similar for all the clades except B3, so the parametric bootstrap approach did not reject the sudden expansion model for the other 6 clades (A1, A2, A3, A4, B1, B2). However, the curves obtained from observed vs. expected differences were graphically coincidental only for clades A1, A2 and B1. Overall, the values obtained testing the demographic history of H. strinatii provided weak and sometimes contrasting signals coherently supporting a past expansion only for clades A1 and B1.
The chronogram with the obtained confidence intervals (S1 Fig) showed that all the lineages are of Pleistocenic origin, since the split between the two main clades A and B occurred around 1.87 mya (1.69 ± 0.2). Within clade A, the supported node splitting the sub-clade A4 vs. all the others is dated 534000 ya (± 90000) and within clade B the main split (B3 vs B1+B2) dated back to 427000 ya (± 86000). The differentiation of tip haplotypes (when resolved) occurred mainly within the Last Glacial Maximum period (LGM) between 47000 and 22000 years BP before the onset of deglaciation around 21000 years ago .
Allozyme data analysis
Eight loci of the 33 studied resulted as monomorphic (Nadh-dh, Np, Sod-1, Sod-2, Adk, Lap, Fum, Mpi) while the remaining 25 had from two to four alleles per population (S2 Table). Twenty private or rare alleles were found, 17 of which were from populations from the Central-Western part of the range (CW, samples 15–30). The same CW populations showed higher levels of genetic variation than the Eastern samples (E, samples 1–14). The values of the observed heterozygosity ranged from 0.021 to 0.112 in the CW samples and between 0.007 and 0.068 in the E ones, with the respective mean values of 0.073 vs. 0.020 significantly differing (p = 0.0001). Similarly the allelic richness was between 1.121 and 1.112 in CW samples, while the E samples provided lower values between 1.011 and 1.054, with the respective mean values of 1.025 vs. 1.076 significantly differing (p = 0.0001) (Table 4). Sampled populations were all in Hardy-Weinberg equilibrium except three that showed a heterozygote deficiency at locus Pep-D. Linkage disequilibrium was calculated for pairwise loci across all populations and no loci pairs showed significant linkage disequilibrium after Bonferroni correction (p < 9.5 x 105).
Assignment tests using the Bayesian model-based analysis implemented in STRUCTURE subdivided the studied samples into five clusters (K = 5) as indicated by both the highest value of ΔK (S2 Fig) and by the plateau of the estimated Ln probability. The analysis carried out with BAPS, despite finding the best value for K = 13, reached the plateau for the associated log(ml) between K = 5 and K = 6. The five clusters recovered were geographically consistent and largely in agreement with the groups identified by haplotype analyses (Fig 4). The eastern samples were grouped in two clusters: one comprising samples from 1 to 11 (corresponding to mtA1), and another including samples 12–14 from the “Rapallo area” corresponding to mtA2. The samples 4, 6 and 11 (SCG, STS, SAL) showed some degree of admixture between these two groups. The samples from the “Finalese” area (15–18) were assigned to a cluster corresponding to mtA3, with nearly no admixture, while those from the “Roburent” area (19–21) formed a fourth cluster corresponding to mtA4. The clusters from the westernmost part of the range merged together, including the samples from “San Bartolomeo Hills”, Tenarda and the Maritime French Alps (corresponding to mitochondrial sub-clusters mtB1, mtB2 and mtB3, respectively). Various degrees of admixture were shown and, in particular, all the individuals from population 25 (STE) were strongly admixed with clusters A1 and A3.
Assignment test of specimens (one per column) to the K = 5 clusters identified by the software STRUCTURE based on the 33 scored allozyme loci. Specimens with admixed genomes are identified by columns showing different colours proportional to the percentage of the genome assigned to each of the 5 clusters.
A Principal Component Analysis (PCA) explained 61.0% of variation with two axes, with the first axis explaining 40.6% of variation (p = 0.009). PCA recovered the larger part of the clusters identified by STRUCTURE (Fig 5), the only exceptions being the easternmost samples (clusters mtA1 + mtA2), which were lumped together. The samples from the Finalese area (15–18, cluster mtA3), which showed no admixed genotypes, were clearly separated, while the samples 24 and 25 (STC, STE) showed an intermediate position in accordance with the high level of admixture shown by the assignment analysis.
Population groups are identified using the same colours as in Fig 1, except for samples 24 (STC) and 25 (STE) which has been left unmarked.
The AMOVA carried out took into consideration the five clusters inferred from STRUCTURE analysis (Table 2) and showed that the within populations and the between clusters levels mostly contributed to the total variation (47% and 38%, respectively, p < 0.0001 for both), while a smaller but significant fraction of total variation was recovered among populations within the groups (15%, p < 0.0001).
The pairwise Fst estimates were always highly significant except when comparing samples from the eastern part of the range (1–11) where only 21 comparisons out of 55 were significant (S2 Table). The overall Fst was 0.54 and the highest values (above 0.70) were recorded when comparing the samples from the “Finalese” (15–18) vs. all the others with particularly high values vs. the eastern samples (even above 0.80). To investigate the correspondence of population genetic structuring to a model of IBD, Fst and geographic distance values were compared by a Mantel test. The results obtained showed a positive correlation across the whole range of the species (r = 0.192, p = 0.0009) as well as within the eastern part of the range (samples 1–14, r = 0.351, p = 0.0080), while IBD did not hold for the central-western populations.
Evolutionary process and diversification in H. strinatii
The results obtained, irrespective of the marker used, showed substantial geographical structuring in H. strinatii despite the small range size. Large genetic divergence over small geographic scales is quite common in plethodontids, especially if living in geographically old areas . However, the geographic pattern of diversity shown in H. strinatii is not homogeneous across its range suggesting different processes leading to the extant Eastern (E, 1–14), and Central-Western (CW, 15–30) population groups. Different levels of genetic variation in the E vs. CW populations were concordantly revealed by both mt and nc markers with E populations characterized by a low level of genetic diversity. A single main haplotype is shared by the larger part of E samples within each of the two sub-clades living in this area (A1, A2) together with a few rare singleton differentiated haplotypes. Also, the lowest values for allozyme variability parameters are recorded from these populations irrespective of the sample size. The pattern of differentiation between E populations conforms to the IBD model, linking genetic and geographic distances along a NW-SE axis. Since small population size and low gene flow, which are usually invoked to explain low genetic variation , are general features of Hydromantes, they cannot account for the lower genetic variation of the E H. strinatii populations. Our data rather support the idea that this pattern is due to a recent expansion in the E part of the range: significance of neutrality tests and mismatch analysis, low genetic variability, the presence of a few, widespread haplotypes and the geographic pattern of genetic diversification following an “expansion route”, are all in agreement with a recent expansion event [66–68].
In the CW part of the range our data highlighted a higher genetic fragmentation. Nearly each population has its own haplotype, and all the Fst values for pairwise comparisons are highly significant. The IBD model does not hold in this area: there is no relationship between genetic and geographic distance with highly differentiated sample pairs found in the range of a few kilometres. Both nc and mt markers identified 3 groups in the C part of the range, but in the W area, the two data sets showed some incongruence. The samples from the “Finalese” (15–18) formed a monophyletic group with the E samples according to mt data, while the same populations resulted as the most differentiated according to the allozymes (Fig 5). In the W part of the range (samples 22–30) the allozymes identified one sub-clade vs. the two recovered by mt data with the allozyme cluster characterized by high admixture levels (Fig 4). This incongruence between mt and nc data can be explained by secondary contacts between differentiated lineages possibly coupled with sex biased dispersal, which is a hypothesis that has been frequently used to reconcile contrasting patterns of nc and mt markers in plethodontids. Allopatric divergence is considered a rule in salamanders, since their low vagility promotes genetic fragmentation as soon as a species disperses over a relatively wide area, especially if this is characterized by complex orography and paleogeographic history . Higher mutation rates and smaller population sizes of mt vs. nc genes would account for the deeper differentiation achieved by mt, while the frequent phylopatry of female salamanders with respect to males would make nc genes merging faster than mt ones . Thus, in many plethodontids allozymes are supposed to reflect recent and ongoing interactions between taxa and populations (i.e., are able to highlight contact zones and gene flow), while mtDNA bears the signature of ancient, deep events [64,70]. Recent data show a broad correspondence between the presence of “misplaced” haplotypes into a nuclear gene pool with introgression events and interpreting the cito-nuclear discordance as support for the mito-genome introgression hypothesis [71–73]. Accordingly, experimental data showed that in Hydromantes species introgression may lead to the capture of “foreign” haplotypes into the gene pool of one species although maintaining differentiated nuclear genomes . In this view, the nesting of the “Finalese” group into the mitochondrial subclade A opposed to its external position according to nuclear data can be explained by a contact between the two sub-clades followed by mtDNA introgression into the “Finalese” populations. Secondary contacts may also be invoked to explain the admixture occurring throughout the westernmost neighbouring sub-clades, where the clear diversification of mt lineages B1, B2 and B3 is coupled with nuclear admixture in the same samples (22–30) and where the highly divergent “Finalese” genome components (orange bars in Fig 4) are found in the admixed and geographically close samples 20 and 19, this latter located less than 10 kilometres far from the nearest sample from the “Finalese” group (pop. n. 16, mtA3) and on the same karstic formation (named “Dolomie di San Pietro ai Monti”). However, part of the admixture observed in these samples (22–30) was due to E alleles (green bars in populations 20–21, 25, 28–29; Fig 4). In this case secondary contacts are unlikely, since they would postulate exchanges between geographically distant groups, so that the retention of ancestral polymorphism seems to be a more likely hypothesis. Accordingly, the signature observed in the westernmost part of the range is that typical of incomplete lineage sorting: high genetic variation is coupled with the coexistence of differentiated clades in the same area as a result of the coalescent process making alleles present in the common ancestor still retained in descendent lineages. Since it is a stochastic process, shared alleles are expected to be randomly distributed in the descendant populations instead of being concentrated along the boundaries between the lineages, as would be the case if secondary contacts would occur, and is in agreement with the pattern reported for H. strinatii [75,76].
The combined effects of paleoclimatic conditions and localized refugia in H. strinatii
The data presented showed high levels of genetic heterogeneity in H. strinatii: most localities had their own haplotypes and even allozymes were able to show highly differentiated populations over a few kilometres. This is in agreement with both literature data, since a strong geographic structure is typical of Hydromantes, and the biological and ecological features of the species characterized by low dispersal and high fragmentation [14,15,17,77]. However, the very same features are apparently in contrast with the high levels of genetic diversity recorded. Long evolutionary history and large, stable population size are frequently identified as the mechanisms generating and maintaining high genetic diversity, and are also recognized in plethodontid salamanders as for example Batrachoseps major . This is not the case for H. strinatii, which has very small populations with a census size usually in the order of tens [10,16] and a relatively recent history of diversification when compared to other plethodontids showing similar genetic patterns. Here the split between the clades A and B goes back about 1.7 million years ago and the diversification within each of the two is dating between 427 ka and 534 ka years ago, while much longer divergence times characterize the main clades of other plethodontid species [18,78]. The co-occurrence of different evolutionary processes as secondary contacts and incomplete lineage sorting may help explaining the high levels of genetic diversity recorded in H. strinatii but other factors are likely to contribute too. Populations of Hydromantes may persist for a long time showing a stable demography despite their small size thanks to their association with subterranean retreats. The importance of localized refugia in shaping the genetic structure of species has recently been stressed in a variety of organisms from plethodontids  to invertebrates [80–82] and plants [3,4,83]. Within this context, the uniqueness of troglophiles species starts emerging. Since they are able to live in both epigean and subterranean habitats, they can manage to maintain their small populations stable and safe in the face of paleoclimatic changes so retaining their own genetic diversity. High haplotype and nucleotide diversity is the signature of historically stable populations and has been recently interpreted as the inheritance of localized refugia when associated with high geographic structuring and a lack of population expansion [2,84]. These expectations are satisfied by our data from the CW sub-clades of H. strinatii, which showed strong genetic/geographic structuring, high haplotipic and nucleotidic diversity and no signs of recent expansion. This witnesses a prolonged persistence of these populations in their cave retreats but further considerations on the peculiar paleoclimatic history of the area may add to the general picture. The Ligurian and Maritime Alps are well known glacial refugia since these areas remained at the borders of the ice sheets during Pleistocene glaciations [21,85–89]. Recent studies have shown that these kind of glacial refugia in both the Roya Valley (Maritime French Alps) and in the “Finalese” are characterized by high levels of species richness and endemism occurrence and by high genetic variation of local populations as was observed in H. strinatii [19,21,86]. The bulk of data produced in the last years added a new scenario to the classical one, which interpreted the high genetic diversity of populations from the Maritime and Ligurian Alps as due to secondary contacts between the Italian peninsular and European lineages [62,90,91]. According to recent data, the Maritime and Ligurian Alps are interpreted as a further glacial refugium and are thus characterized by a high genetic variation of local populations, which persisted here even during the Last Glacial Maximum and then gave birth to hybridization between locally originated lineages as witnessed by H. strinatii too [22,24,92].
The study of mt and nc markers in H. strinatii provided a complex picture, suggesting that the action of different evolutionary processes could be identified despite the low population size typical of this species enhancing the effects of the genetic drift and thus introducing some randomness in the general pattern of variation.
In the CW part of the range, the observed phylogeographic pattern is in agreement with the persistence of local populations due both to the paleoclimatic history of the Ligurian and Maritime Alps, which remained sheltered from ice cover during the Pleistocene glacial episodes, and to the troglophyle habits of the species that is able to use subterranean retreats when climatic conditions become too harsh. The maintenance of high genetic variation is due to the co-occurrence of different mechanisms. These include isolation, promoting divergence and therefore producing clearcut differences in allele frequencies as is the case in the highly isolated “Finalese” area, but also nuclear admixture and mt introgression through secondary contact between geographically nearby lineages. Therefore, in these populations the retention of polymorphism through small populations stability seems to be a relevant mechanism explaining their high genetic variation. This finding strengthens the idea that persistence in small, localized refugia may act efficaciously on tightly associated species in maintaining unusually high levels of genetic diversity through the retention of genetic variation at the intrapopulation level and through the maintenance of any new genotype acquired in the localized refugia.
S1 Fig. Mitochondrial chronogram for H. strinatii.
Maximum clade credibility tree obtained from the mitochondrial dataset. Red bars at nodes represent the 95% Highest Posterior Densities of node ages. The split node between H. strinatii and Eastern Sardinian species (H. supramontis and H. imperialis) was constrained at 5.33 ma, which is the end of the Messinian salinity crisis.
S2 Fig. Results from the ∆K analysis.
S1 Table. List of allozyme loci scored on H. strinatii.
S2 Table. Allozyme allele frequencies in H. strinatii.
Allozyme allele frequencies per population at the 25 polymorphic loci out of the 33 scored.
S3 Table. Pairwise Fst values.
Pairwise fixation index (Fst) values based on allozyme data. * p <0.05; ** p < 0.01; *** p < 0.001;—not significant
S1 File. Optimal clustering in H. strinatii.
Plot of the number of groups (K) obtained: (a) by plotting Fct vs. K values according to SAMOVA (mt data); (b) by plotting log marginal likelihood vs. K values according to BAPS (b1, mt data; b2, nuclear data).
We are indebted to professor B. Lanza, who inspired all our work on Hydromantes, besides providing nearly all the studied specimens. We thank Dr. D. Canestrelli for his useful observations on an early draft of this manuscript and Dr. C. Carere for reviewing English.
Conceived and designed the experiments: RC DL GN. Performed the experiments: RC DL. Analyzed the data: RC DL. Contributed reagents/materials/analysis tools: RC GN. Wrote the paper: RC DL.
- 1. Culver DC, Master LL, Christman MC, Hobbs HH. Obligate Cave Fauna of the 48 Contiguous United States. Conser Biol. 2000; 14: 386–401.
- 2. Bryson RW Jr, Prendini L, Savary WE, Pearman PB. Caves as microrefugia: Pleistocene phylogeography of the troglophilic North American scorpion Pseudouroctonus reddelli. BMC Evol Biol. 2014; 14: 9. pmid:24428910
- 3. Tapper SL, Byrne M, Yates CJ, Keppel G, Hopper SD, Van Niel K, et al. Isolated with persistence or dynamically connected? Genetic patterns in a common granite outcrop endemic. Diversity Distrib. 2014(a); 20: 987–1001.
- 4. Tapper SL, Margaret B, Yates CJ, Keppel G, Hopper SD, Van Niel K, et al. Prolonged isolation and persistence of a common endemic on granite outcrops in both mesic and semi-arid environments in south-western Australia. J Biogeogr. 2014(b); 41: 2032–2044.
- 5. Weber LC, VanDerWal J, Schmidt S, McDonald WJF, Shoo LP. Patterns of rain forest plant endemism in subtropical Australia relate to stable mesic refugia and species dispersal limitations. J Biogeogr. (2014); 41: 222–238.
- 6. Ashcroft MB, Gollan JR, Warton DI, Ramp D. A novel approach to quantify and locate potential microrefugia using topoclimate, climate stability, and isolation from the matrix. Glob Change Biol. 2012; 18: 1866–1879.
- 7. Beheregaray LB. Twenty years of phylogeography: the state of the field and the challenges for the Southern Hemisphere. Mol Ecol. 2008; 17: 3754–3774. pmid:18627447
- 8. Garrick RC. Montane refuges and topographic complexity generate and maintain invertebrate biodiversity: recurring themes across space and time. J Insect Conserv. 2011; 15: 469–478.
- 9. Keppel G, Van Niel KP, Wardell-Johnson GW, Yates CJ, Byrne M, Mucina L, et al. Refugia: identifying and understanding safe havens for biodiversity under climate change. Global Ecol Biogeogr. 2012; 21: 393–404.
- 10. Cimmaruta R, Forti G, Nascetti G, Bullini L. Spatial distribution and competition in two parapatric sibling species of European plethodontid salamanders. Ethol Ecol Evol. 1999; 11: 383–398.
- 11. Lanza B, Caputo V, Nascetti G, Bullini L. Morphologic and genetic studies on the European plethodontid salamanders: taxonomic inferences (genus Hydromantes). Torino: Monografie XVI, Museo Regionale Scienze Naturali;1995.
- 12. Lunghi E, Manenti R, Manca S, Mulargia M, Pennati R, Ficetola GF. Nesting of cave salamanders (Hydromantes flavus and H. italicus) in natural environments. Salamandra. 2014; 50: 105–109.
- 13. Salvidio S, Lattes A, Tavano M, Melodia F. Ecology of a Speleomantes ambrosii population inhabiting an artificial tunnel. Amphibia-Reptilia. 1994; 15: 35–45.
- 14. Chiari Y, van der Meijden A, Mucedda M, Lourenço JM, Hochkirch A, Veith M. Phylogeography of sardinian cave salamanders (genus Hydromantes) is mainly determined by geomorphology. PLoS ONE. 2012; 7: e32332. pmid:22427830
- 15. Nascetti G, Cimmaruta R, Lanza B, Bullini L. Genetic and geographic variation in the European plethodontid salamanders (genus Hydromantes). J Herpetol. 1996; 30: 161–183.
- 16. Salvidio S. Homing behaviour in Speleomantes strinatii (Amphibia Plethodontidae): a preliminary displacement experiment. N West J Zool. 2013; 9: 429–432.
- 17. Carranza S, Romano A, Arnold EN, Sotgiu G. Biogeography and evolution of European cave salamanders, Hydromantes (Urodela: Plethodontidae), inferred from mtDNA sequences. J Biogeogr. 2008; 35: 724–738.
- 18. Vieites DR, Min MS, Wake DB. Rapid diversification and dispersal during periods of global warming by plethodontid salamanders. Proc Natl Acad Sci USA. 2007; 104: 19903–19907. pmid:18077422
- 19. Casazza G, Zappa E, Mariotti MG, Médail F, Minuto L. Ecological and historical factors affecting distribution pattern and richness of endemic plant species: the case of the Maritime and Ligurian Alps hotspot. Diversity Distrib. 2008; 14: 47–58.
- 20. Casazza G, Zappa E, Mariotti MG, Médail F, Minuto L. Distribution pattern and richness of endemic plant species in Maritime and Ligurian Alps. Boll Mus Ist Biol Univ Genova. 2010; 72: 130–136.
- 21. Grassi F, Minuto L, Casazza G, Labra M, Sala F. Haplotype richness in refugial areas: phylogeographical structure of Saxifraga callosa. J Plant Res. 2009; 122: 377–387. pmid:19363647
- 22. Garnier S, Alibert P, Audiot P, Prieur B, Rasplus J- Y. Isolation by distance and sharp discontinuities in gene frequencies: implications for the phylogeography of an alpine insect species, Carabus solieri. Mol Ecol. 2004; 13: 1883–1897. pmid:15189211
- 23. Habel JC, Schmitt T, Muller P. The fourth paradigm pattern of post-glacial range expansion of European terrestrial species: the phylogeography of the Marbled White butterfly (Satyrinae, Lepidoptera). J of Biogeogr. 2005; 32: 1489–1497.
- 24. Rousselet J, Zhao R, Argal D, Simonato M, Battisti A, Roques A, et al. The role of topography in structuring the demographic history of the pine processionary moth, Thaumetopoea pityocampa (Lepidoptera: Notodontidae). J Biogeogr. 2010; 37: 1478–1490.
- 25. Doyle J J, Doyle J L. A rapid DNA isolation procedure for small quantities of fresh leaf tissue. Phytochem Bull. 1987; 19: 11–15.
- 26. Thompson JD, Gibson TJ, Plewniak F, Jeanmougin F, Higgins DG. The ClustalX windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res. 1997; 25: 4876–4882. pmid:9396791
- 27. Silvestro D, Michalak I. raxmlGUI: A graphical front-end for RAxML Org Divers Evol. 2011; 12: 335–337.
- 28. Ronquist F, Teslenko M, van der Mark P, Ayres DL, Darling A, Höhna S, et al. MrBayes 32: Efficient Bayesian phylogenetic inference and model choice across a large model space. Syst Biol. 2011; 61: 539–542.
- 29. Darriba D, Taboada GL, Doallo R, Posada D. jModelTest 2: more models, new heuristics and parallel computing. Nat Methods. 2012; 9: 772.
- 30. Rambaut A, Suchard MA, Xie W, Drummond A. Tracer v1.6. 2013. Available: http://treebioedacuk/software/tracer/.
- 31. Xia X, Yang Q. A distance-based least-square method for dating speciation events. Mol Phylogenet Evol. 2011; 59: 342–353. pmid:21320613
- 32. Xia X. DAMBE5: A comprehensive software package for data analysis in molecular biology and evolution. Mol Biol Evol. 2013; 30:1720–1728. pmid:23564938
- 33. Hsü KJ, Ryan WBF, Cita MB. Late Miocene desiccation of the Mediterranean. Nature. 1973; 242: 40–244.
- 34. Krijgsman W, Hilgen FJ, Raffi I, Sierro FJ, Wilson DS. Chronology, causes and progression of the Messinian salinity crisis. Nature. 1999; 400: 652–655.
- 35. Bandelt HJ, Forster P, Rohl A. Median-joining networks for inferring intraspecific phylogenies. Mol Biol Evol. 1999; 16:37–48. pmid:10331250
- 36. Foulds LR, Hendy MD, Penny D. A graph theoretic approach to the development of minimal phylogenetic trees. J Mol Evol. 1979: 13: 127–149. pmid:480370
- 37. Tamura K, Dudley J, Nei M, Kumar S. MEGA: Molecular Evolutionary Genetic Analysis (MEGA) software version 4.0. Mol Biol Evol. 2007; 24: 1596–1599. pmid:17488738
- 38. Kimura M. A simple model for estimating evolutionary rates of base substitutions between homologous nucleotide sequences. J Mol Evol. 1980; 16:111–20. pmid:7463489
- 39. Dupanloup I, Schneider S, Excoffier L. A simulated annealing approach to define the genetic structure of populations. Mol Ecol. 2002; 11: 2571–2581. pmid:12453240
- 40. Cheng L, Connor TR, Sirén J, Aanensen DM, Corander J. Hierarchical and spatially explicit clustering of DNA sequences with BAPS Software. Mol Biol Evol. 2013; 30: 1224–1228. pmid:23408797
- 41. Corander J, Tang J. Bayesian analysis of population structure based on linked molecular information Math Biosci. 2007; 205: 19–31. pmid:17087977
- 42. Corander J, Marttinen P, Sirén J, Tang J. Enhanced Bayesian modelling in BAPS software for learning genetic structures of populations. BMC Bioinformatics. 2008(a); 9: 539. pmid:19087322
- 43. Librado P, Rozas J. DnaSP v.5: A software for comprehensive analysis of DNA polymorphism data. Bioinformatics. 2009; 25: 1451–1452. pmid:19346325
- 44. Excoffier L, Smouse PE, Quatto JM. Analysis of molecular variance inferred from metric distances among DNA haplotypes: application to human mitochondrial DNA restriction data. Genetics. 1992; 131: 479–491. pmid:1644282
- 45. Excoffier L, Lischer HEL. Arlequin suite ver 3.5: A new series of programs to perform population genetics analyses under Linux and Windows. Mol Ecol Resour. 2010; 10: 564–567. pmid:21565059
- 46. Tajima F. Statistical method for testing the neutral mutation hypothesis by DNA polymorphism. Genetics. (1989); 123: 585–595. pmid:2513255
- 47. Fu YX. Statistical tests of neutrality of mutations against population growth, hitchhiking and background selection. Genetics. 1997; 147: 915–925. pmid:9335623
- 48. Ramos-Onsins SE, Rozas J. Statistical properties of new neutrality tests against population growth. Mol Biol and Evol. 2002; 19: 2092–2100.
- 49. Slatkin M, Hudson RR. Pairwise comparisons of mitochondrial DNA sequences in stable and exponentially growing populations. Genetics. 1991; 129: 555–562. pmid:1743491
- 50. Harpending HC, Sherry ST, Rogers AR, Stoneking M. The genetic structure of ancient human populations. Curr Anthropol. 1993; 34: 483–496.
- 51. Harpending HC. Signature of ancient population growth in a low-resolution mitochondrial DNA mismatch distribution. Hum Biol. 1994; 66: 591–600. pmid:8088750
- 52. Raymond M, Rousset F. GENEPOP (version 12): population genetics software for exact tests and ecumenicism. J Hered. 1995; 86: 248–249.
- 53. Belkhir K, Borsa P, Chikhi L, Raufaste N, Bonhomme F. GENETIX 4.02, logiciel sous windows TM pour la génétique des populations Laboratoire Génome, Population, Interactions: CNRS UMR 5000. Montpellier: Université de Montpellier II. France Biosciences. 2001; 205: 19–31.
- 54. Meirmans PG, Van Tienderen PH. GENOTYPE and GENODIVE: two programs for the analysis of genetic diversity of asexual organisms. Mol Ecol Notes. 2004; 4: 792–794.
- 55. Goudet J. FSTAT (version 1.2): a computer program to calculate F-statistics. J Hered. 1995; 86: 485–486. Available: http://www2.unil.ch/popgen/softwares/fstat.htm.
- 56. Rice W. Analyzing tables of statistical tests. Evolution. 1989; 43: 223–225.
- 57. Corander J, Sirén J, Arjas E. Bayesian Spatial Modelling of Genetic Population Structure. Comput Stat. 2008(b); 23: 111–129.
- 58. Pritchard JK, Stephens M, Donnelly P. Inference of population structure using multilocus genotype data. Genetics. 200; 155: 945–959. pmid:10835412
- 59. Evanno G, Regnaut S, Goudet J. Detecting the number of clusters of individuals using the software STRUCTURE: a simulation study. Mol. Ecol. 2005; 14: 2611–2620. pmid:15969739
- 60. Earl DA, vonHoldt BM. STRUCTURE HARVESTER: a website and program for visualizing STRUCTURE output and implementing the Evanno method. Conserv Genet Resour. 2012; 4: 359–361.
- 61. Jakobsson M, Rosenberg NA. CLUMPP: a cluster matching and permutation program for dealing with label switching and multimodality in analysis of population structure. Bioinformatics. 2012; 23: 1801–1806.
- 62. Rosenberg NA. Distruct: a program for the graphical display of population structure. Mol Ecol Notes 2004; 4: 137–138.
- 63. Ivy-Ochs S, Kerschner H, Reuther A, Maisch M, Sailer R, Schaefer R, et al. The timing of glacier advances in the northern European Alps based on surface exposure dating with cosmogenic 10Be, 26Al, 36Cl, and 21Ne. Geol Soc Am. 2006: 415: 43–60.
- 64. Jockush EL, Wake DB. Falling apart and merging: diversification of slender salamanders (Plethodontidae: Batrachoseps) in the American West. Biol J Linn Soc. 2002; 76: 361–391.
- 65. Amos W, Harwood J. Factors affecting levels of genetic diversity in natural populations. Phil Trans R Soc Lond B. 1998; 353: 177–186.
- 66. Hewitt GM. The genetic legacy of the Quaternary ice ages. Nature. 2000: 405: 907–913. pmid:10879524
- 67. Hewitt GM. Genetic consequences of climatic oscillations in the Quaternary. Phil Trans R Soc Lond. 2004; 359: 183–195.
- 68. Ibrahim KM, Nichols RA, Hewitt GM. Spatial patterns of genetic variation generated by different forms of dispersal during range expansion. Heredity. 1996; 77: 282–291.
- 69. Liebgold EB, Brodie ED, Cabe PR. Female philopatry and male-biased dispersal in a direct-developing salamander, Plethodon cinereus. Mol Ecol. 2011; 20: 249–257. pmid:21134012
- 70. Weisrock DW, Kozak KH, Larson A. Phylogeographic analysis of mitochondrial gene flow and introgression in the salamander, Plethodon shermani. Mol Ecol. 2005; 14: 1457–1472. pmid:15813784
- 71. Arnold ML. Natural Hybridization and Evolution. New York: Oxford Univ Press. 1997
- 72. Qi Y, Lu B, Gao H, Hu P, Fu J. Hybridization and mitochondrial genome introgression between Rana chensinensis and R. kukunoris. Mol Ecol. 2014; 23: 5575–88. pmid:25308955
- 73. Toews DPL, Brelsford A. The biogeography of mitochondrial and nuclear discordance in animals. Mol Ecol. 2012; 21: 3907–3930. pmid:22738314
- 74. Cimmaruta R, Forti G, Lucente D, Nascetti G. Thirty years of artificial syntopy between Hydromantes italicus and H. ambrosii ambrosii (Amphibia, Plethodontidae). Amphibia-Reptilia. 2013; 34: 413–420.
- 75. Barbujani G, Pilastro A, De Domenico S, Renfrew C. Genetic variation in North Africa and Eurasia: Neolithic demic diffusion vs paleolithic colonization. Am J Phys Anthropol. 1994; 95: 137–154. pmid:7802092
- 76. Funk DJ, Omland KE. Species level paraphyly and polyphyly: frequency, causes, and consequences, with insights from animal mitochondrial DNA. Annu Rev Ecol Evol Syst. 2003; 34: 397–423.
- 77. Van der Meijden A, Chiari Y, Mucedda M, Carranza S, Corti C, Veith M. Phylogenetic relationships of Sardinian cave salamanders, genus Hydromantes, based on mitochondrial and nuclear DNA sequence data. Mol Phylogenet Evol. 2009; 51: 399–404. pmid:19136065
- 78. Martínez-Solano Í, Peralta-García A, Jockusch EL, Wake DB, Vázquez-Domínguez E, Parra-Olea G. Molecular systematics of Batrachoseps (Caudata, Plethodontidae) in southern California and Baja California: Mitochondrial-nuclear DNA discordance and the evolutionary history of B major. Mol Phylogenet Evol. 2012; 63:131–149. pmid:22285301
- 79. Niemiller ML, Fitzpatrick BM, Miller BT. Recent divergence-with-gene-flow in Tennessee cave salamanders (Plethodontidae: Gyrinophilus) inferred from gene genealogies. Mol Ecol. 2008;17: 2258–2275. pmid:18410292
- 80. Allegrucci G, Todisco V, Sbordoni V. Molecular phylogeography of Dolichopoda cave crickets (Orthoptera, Rhaphidophoridae): a scenario suggested by mitochondrial DNA. Mol Phylogenet Evol. 2005; 37: 153–164. pmid:15964214
- 81. Derkarabetian S, Steinmann DB, Hedin M. Repeated and Time-Correlated Morphological Convergence in Cave-Dwelling Harvestmen (Opiliones, Laniatores) from Montane Western North America. Plos One. 2010; 5: e10388. pmid:20479884
- 82. Snowman CV, Zigler KS, Hedin M. Caves as islands: mitochondrial phylogeography of the cave-obligate spider species Nesticus barri (Araneae: Nesticidae). J Arachnology. 2010; 38: 49–56.
- 83. Kropf M, Kadereit JW, Hans Peter Comes HP. Late Quaternary distributional stasis in the submediterranean mountain plant Anthyllis montana L (Fabaceae) inferred from ITS sequences and amplified fragment length polymorphism markers. Mol Ecol. 2002; 11: 447–463. pmid:11918780
- 84. Mosblech NAS, Bush MB, van Woesik R. On metapopulations and microrefugia: palaeoecological insights. J Biogeogr. 2011; 38: 419–429.
- 85. Diadema K, Bretagnolle F, Affre L, Yuan Y, Medail F. Geographic structure of molecular variation of Gentiana ligustica (Gentianaceae) in the Maritime and Ligurian regional hotspot, inferred from ITS sequences. Taxon. 2005; 54: 887–894.
- 86. Minuto L, Grassi F, Casazza G. Ecogeographic and genetic evaluation of endemic species in the Maritime Alps: the case of Moehringia lebrunii and M sedoides (Caryophyllaceae). Plant Biosyst. 2006; 140: 146–155.
- 87. Schönswetter P, Stehlik I, Holderegger R, Tribsch A. Molecular evidence for glacial refugia of mountain plants in the European Alps. Mol Ecol. 2005; 14: 3547–3555. pmid:16156822
- 88. Stefani F, Gentilli A, Sacchi R, Razzetti E, Pellitteri-Rosa D, Pupin F, et al. Refugia within refugia as a key to disentangle the genetic pattern of a highly variable species: the case of Rana temporaria Linnaeus, 1758 (Anura, Ranidae). Mol Phylogenet Evol. 2012; 65: 718–726. pmid:22874474
- 89. Zecca G, Casazza G, Minuto L, Labra M, Grassi F. Allopatric divergence and secondary contacts in Euphorbia spinosa L: influence of climatic changes on the split of the species. Org Divers Evol. 2011; 11: 357–372.
- 90. Petit RJ, Aguinagalde I, de Beaulieu J-L, Bittkau C, Brewer S, Cheddadi R, et al. Glacial refugia: hotspots but not melting pots of genetic diversity. Science. 2003; 300: 1563–1565. pmid:12791991
- 91. Taberlet P, Fumagalli L, Wust-Saucy AG, Cosson JF. Comparative phylogeography and postglacial colonization routes in Europe. Mol Ecol. 1988; 7: 453–464.
- 92. Casazza G, Grassi F, Zecca G, Mariotti MG, Guerrina M, Minuto L. Phylogeography of Primula allionii (Primulaceae), a narrow endemic of the Maritime Alps. Bot J Linn Soc. 2013; 173: 637–653.