When a population shows a marked morphological change, it is important to know whether that population is genetically distinct; if it is not, the novel trait could correspond to an adaptation that might be of great ecological interest. Here, we studied a subspecies of water shrew, Neomys fodiens niethammeri, which is found in a narrow strip of the northern Iberian Peninsula. This subspecies presents an abrupt increase in skull size when compared to the rest of the Eurasian population, which has led to the suggestion that it is actually a different species. Skulls obtained from owl pellets collected over the last 50 years allowed us to perform a morphometric analysis in addition to an extensive multilocus analysis based on short intron fragments successfully amplified from these degraded samples. Interestingly, no genetic divergence was detected using either mitochondrial or nuclear data. Additionally, an allele frequency analysis revealed no significant genetic differentiation. The absence of genetic divergence and differentiation revealed here indicate that the large form of N. fodiens does not correspond to a different species and instead represents an extreme case of size increase, of possible adaptive value, which deserves further investigation.
Phylogeographic studies allow researchers to understand not only the geographical distribution of genetic diversity, but also the evolution of phenotypic differences that might have adaptive potential1,2. Changes in body size are among the most important sources of phenotypic variation in endothermic vertebrates3,4. They can occur across a clinal variation as a consequence of the changing environment5, in islands due to ecological release6, or be restricted to a limited region within a species’ range due to local adaptation7. In some of these cases, populations with different body sizes are recognized as subspecies. Other instances of body-size modification in specific areas do not result in taxonomic changes as they are likely to correspond to ecotypes that can exploit new resources, more accessible to individuals with either smaller or larger body sizes8,9,10. Understanding the origin and evolution of such body size changes and whether these arose through a process of isolation or a rapid ecological adaptation requires a thorough phylogeographic and population genetics analysis, something that many studies on this topic lack.
The Eurasian water shrew (Neomys fodiens) is a good example of where the relationship between body size variation and phylogeography can be studied. This species has a Eurasian distribution, ranging from the northern Iberian Peninsula to eastern Asia11. It is a semi-aquatic species that inhabits water courses and other wetland habitats with abundant invertebrate prey11,12. Among the four species described in the genus13, N. fodiens is considered the most aquatic due to its excellent diving ability, although it sometimes demonstrates terrestrial behavior12,14.
Several subspecies have been proposed for N. fodiens, but none has been adequately assessed, with the exception of N. f. niethammeri15. This taxon is present in the north-central Iberian Peninsula, from the Cantabrian Range to the western end of the Pyrenees (Supplementary Fig. S1)16,17,18,19, and is characterized by the largest skull size observed throughout the range of N. fodiens19. This size increase in a specific population is striking, as the morphology of this species is fairly stable across the rest of its European range20. N. f. niethammeri lives sympatrically with N. anomalus21, which was recently separated from the European species N. milleri13,22. A population of the nominal subspecies N. f. fodiens is found beyond the range of N. f. niethammeri12, making that the population of N. f. niethammeri is flanked by populations of N. f. fodiens (Supplementary Fig. S1). Coronoid height has been widely used to differentiate Neomys species in paleontological and neontological studies17,23,24,25, and is also the main character to distinguish N. f. niethammeri16,17,18,19. Due to the much larger size of the latter, it has been suggested that it is a different species in numerous studies, including the most important reference works on mammals11,15,18,19.
Improved laboratory techniques, many adopted from ancient DNA studies that target low quality and degraded DNA, have enabled the use of non-invasive and minimally invasive samples as well as different types of post mortem remains in phylogeographic studies26,27. This has made it possible to genetically analyze elusive and threatened species, as larger sample sets that do not require the manipulation or capture of specimens become available for study22,28,29. For example, skull bones obtained from owl pellets containing undigested material from small mammal prey have been used in various phylogeographic studies30,31,32. This material is very interesting as it can be used for both morphological and genetic work. However, despite this potential, few studies have taken advantage of skull bones from owl pellets for simultaneous genetic and morphometric analyses and, in particular, to recover nuclear data.
Mitochondrial DNA is more abundant than nuclear DNA in animal cells and can be more easily amplified from degraded samples. Nevertheless, mitochondrial introgression, which is a common phenomenon in mammals, may lead to erroneous conclusions if only mitochondrial genes are considered33,34. The development of highly variable nuclear markers avoids the problems of using solely mitochondrial sequences and allows the use of coalescent-based methods35,36, thus leading to robust conclusions on the origin and evolution of biodiversity13,33,37,38. It is therefore important to develop nuclear markers that can be amplified from degraded samples, in which the DNA fragment size is shorter. In order to amplify these short fragments, primers need to be designed to reduce the size of the PCR product so that more DNA becomes available for amplification, thus exploiting the full potential of multilocus information.
The main objective of this work was to understand whether the size increase observed in N. f. niethammeri is linked to genetic distinctiveness. To discern this, we first designed novel nuclear introns that could be amplified using skull bones extracted from barn owl pellets collected over recent decades. From this material we then amplified mitochondrial and nuclear markers, and performed a morphological analysis as well as a multilocus study of genetic divergence, differentiation, and diversity. The results showed that the relationship between phenotypic novelty and phylogeography is not always easily predictable.
Morphometric analyses of Neomys mandibles
Skull samples from 67 Neomys individuals (Supplementary Table S1) were obtained, primarily, from barn owl pellets collected over the last 50 years in the northern Iberian Peninsula. The samples came from approximately longitudes −7° to 2°, where two subspecies of N. fodiens, as well as N. anomalus, are present (Fig. 1). Landmarks were taken from each mandible (Supplementary Appendix S1) to measure the coronoid height and perform a geometric morphometric analysis. According to the coronoid height (Supplementary Fig. S2), 32 samples were classified as N. f. niethammeri, 19 as N. f. fodiens, and 16 as N. anomalus (Supplementary Table S2). Plotting these measurements against longitude, we confirmed an abrupt size increase in N. f. niethammeri in the north-central part of the Iberian Peninsula, approximately between longitudes −6.25° and −1° (Fig. 1c), corroborating previous work17,18. We found individuals of both sizes in the same locality, indicating a certain overlap in the distribution of the two groups. The skulls of the sympatric species N. anomalus were always smaller than those of N. fodiens (Supplementary Table S2). The centroid size of the mandibles provided similar results (Supplementary Fig. S3 and Supplementary Table S2). A principal components analysis of the landmarks allowed N. anomalus to be distinguished from N. fodiens, but not N. f. niethammeri from N. f. fodiens (Fig. 2), indicating that the two N. fodiens subspecies were similar in shape.
Mitochondrial phylogeny of Neomys
Both complete and partial mitochondrial cytochrome b sequences were obtained from 85 samples of N. fodiens, including all the mandibles used in the morphometric analysis plus additional tissue samples from Eurasia (Fig. 1 and Supplementary Table S1). Some primers were newly designed (Supplementary Table S3) so that sequences could be obtained from the majority of samples, including the oldest (Supplementary Table S1). The Bayesian mitochondrial tree reconstructed with the N. fodiens mitochondrial sequences can be subdivided into three main clades separated by relatively long branches and moderate or high support (Fig. 3): one includes the Iberian samples and a sample from a nearby locality in France; the second consists of a single sample from southern Italy; and the third comprises samples from the remaining Eurasian range of the species. Coronoid height measurements mapped into this tree indicated that individuals classified as N. f. niethammeri appeared randomly across the Iberian clade, reflecting the fact that the two subspecies were indistinguishable at the mitochondrial level. When additional sequences from other Neomys species were included in the Bayesian phylogenetic analysis to configure a dataset of 136 sequences, the tree perfectly separated the four species in the genus, but N. f. fodiens and N. f. niethammeri were once again intermixed in the tree (Supplementary Fig. S4). Similar results were obtained with a maximum-likelihood method (Supplementary Fig. S5).
Development of nuclear markers for degraded Neomys samples
We developed a set of six short intron markers (ASB6 intron 2, CSF2 intron 2, GDAP1 intron 1, JMJD intron 2, MYCBPAP intron 11, and TRAIP intron 8) that could be amplified using DNA extracted from the mandibles, despite the high degradation levels of some of them (Supplementary Table S4). For some introns, several rounds of primer design were performed to shorten the PCR product and allow the amplification of the most degraded samples (Supplementary Table S4). In this way, we obtained nuclear information from most of the recent samples, as well as from a good proportion of the older samples, including those collected during the 1970s (Supplementary Table S1). For some introns, allele-specific primers were designed to separate heterozygous sequences (Supplementary Table S5). A total of 58 samples with a minimum of four sequenced introns were used in further analyses, including 37 mandibles and 11 tissues, together with sequences from 10 samples taken from a previous work13 (Supplementary Table S1). Considering all the introns together, 172 sequences were used from N. f. niethammeri, 250 from the other N. fodiens specimens, 158 from N. anomalus, 48 from N. milleri, and 24 from N. teres, totaling 123,556 bp of nuclear sequence information after alignment cleaning (Supplementary Appendix S2).
Multilocus phylogenetic analysis of Neomys
Haplotype genealogies derived from the maximum-likelihood trees of the nuclear sequences showed a low degree of allele sharing between the four Neomys species (Fig. 4a). On the other hand, N. f. niethammeri and the rest of N. fodiens shared the most frequent alleles (largest circles in Fig. 4a), although most minor alleles were exclusive to one group or the other (smaller circles in Fig. 4a). Since the mutational differences between the alleles were minimal, both groups were completely intermixed in the phylogenetic tree reconstructed using the concatenated intron sequences (Fig. 4b). In fact, no clades within N. fodiens can be distinguished in the nuclear tree.
To study the possibility that differentiated groups existed within N. fodiens, we next converted the six intron alignments into a multi-allelic data format. There were 22 different alleles and therefore the average number of alleles per locus was 3.7. Using this information, we calculated the FST distance between N. f. niethammeri, N. f. fodiens from the northern Iberian Peninsula, and N. fodiens from the rest of the range. The value obtained between N. f. niethammeri and Iberian N. f. fodiens was 0.040 and it was not significant (95% confidence interval: −0.005, 0.085). FST values between these and the other population were also non-significant.
Nuclear genetic diversity of N. fodiens populations
Individual heterozygosity estimated from the nuclear introns of N. fodiens specimens showed that the most heterozygous samples were from the northern Iberian Peninsula (Fig. 5). Thus, we found an average of 0.0013 heterozygous positions in the Iberian samples (including both N. f. fodiens and N. f. niethammeri) versus 0.0004 in the rest of the sampled range. When the nuclear data was analyzed at the population level, the average θ values were 0.0021 and 0.0014 for these two groups, respectively (Supplementary Table S6), showing the same trend. The same was found with the π parameter (Supplementary Table S6).
The multilocus dataset used in this study of the Eurasian water shrew Neomys fodiens was based on the mitochondrial cytochrome b gene and six small intron fragments. The lengths of the newly designed introns (153–229 bp) were smaller than those of previously proposed intron markers13,37, in order to facilitate the amplification of degraded DNA obtained from skulls from owl pellet material. Using the novel primers, we amplified between 4 and 6 introns from 37 mandible samples of Neomys, many of which had been collected during the 1970s (Supplementary Table S1). Despite their relatively short lengths, the intron markers were variable enough to detect mutational differences between species. They also enabled the reconstruction of a nuclear phylogenetic tree, which was compared with the mitochondrial tree and used to detect any possible occurrence of mito-nuclear discordance in Neomys. Finally, once these intron markers were converted to allele frequency data, and despite the small number of markers used, they allowed us to undertake a differentiation analysis of the main populations of N. fodiens. Therefore, thanks to the various genetic analyses performed, these novel markers were highly useful in unraveling the evolutionary history of N. f. niethammeri and, specifically, assessing whether the morphological differences observed (large skull size) arose through a long period of isolation and genetic differentiation. Furthermore, to our knowledge, this is one of the first studies where multilocus genetic data as well as morphometric information of skulls obtained from owl pellets has been fully exploited, showing the enormous potential of this type of non-invasive sampling for biodiversity studies.
The mitochondrial sequences of N. f. fodiens and N. f. niethammeri were intermixed in the phylogenetic tree, meaning that there was no evidence to suggest genetic divergence (Figs 3 and S4). This was a highly unexpected result for two populations with important skull size differences. Without further data, a possible explanation could be that, in fact, these two forms were more divergent at the nuclear level but, due to some recent unidirectional introgression event, N. f. niethammeri acquired the mitochondria of N. f. fodiens, a phenomenon that has been observed in many other species33,34. With N. anomalus living sympatrically with N. fodiens in the northern Iberian Peninsula, additional scenarios involving inter-specific introgression with this other species could not be discarded, demonstrating the need to carry out a nuclear analysis. The phylogenetic tree we obtained using nuclear data also revealed a lack of genetic divergence between the two N. fodiens subspecies (Fig. 4b). A first conclusion from this work is, therefore, that our mitochondrial and nuclear data are consistent in highlighting a lack of support for genetic divergence between N. f. fodiens and N. f. niethammeri.
The mitochondrial and nuclear phylogenies showed that the four Neomys species were reciprocally monophyletic in both trees (Figs 4b and S4). This suggests that there has been no recent mitochondrial introgression, not only between N. fodiens groups, but also during the evolution of the Neomys species. Incidentally, the topological relationships between the four Neomys species were not coincident in the mitochondrial and nuclear trees, since N. milleri and N. anomalus group in the former, whereas N. milleri and N. teres appear as sister taxa in the latter. However, this could be a consequence of methodological difficulties in resolving old divergences in the tree or incomplete lineage sorting39, and it does not affect the conclusion that there has been no recent introgression in Neomys. This reasonable mito-nuclear agreement enables the use of cytochrome b for species identification from non-invasive samples in further ecological studies of this genus22.
Populations that have been isolated for a short period of time may not have accumulated enough mutations to reflect phylogenetic separation, but, if the gene flow between them is low, differences in allele frequencies may appear by genetic drift40,41. To test the possibility that N. fodiens populations showed some degree of differentiation, we computed FST statistics. No significant genetic differentiation was found. Thus, the increase in skull size of N. f. niethammeri (Fig. 1c) corresponded to neither a difference in shape (Fig. 2) nor mitochondrial (Fig. 3) or nuclear genetic divergence (Fig. 4b), nor genetic differentiation of nuclear allele frequencies. In this respect, it is interesting to note that fossil data of both forms have been found at ~40 kyr24,25. This would suggest that a large amount of gene flow must have occurred between the two forms to prevent genetic differentiation during all this time, indicating the lack of reproductive barriers between them.
The populations of N. fodiens of the northern Iberian Peninsula are at the edge of the Palearctic range of the species (Supplementary Fig. S1), which could lead to the hypothesis that this area was recently colonized from the multiple European glacial refugia that have been described for various taxa42,43. We found, however, that the nuclear genetic diversity was higher in the Iberian samples than in the rest of the Palearctic samples analyzed here (Fig. 5), something that is not consistent with the recent colonization of the Iberian Peninsula. The existence in this area of fossil N. fodiens dated at ~40 kyr24,25,44 also supports the idea that the species was present in the Iberian Peninsula long before the Last Glacial Maximum and, consequently, that these populations are not the product of recent colonization. Instead, refugia in the Iberian Peninsula or nearby areas were likely to have been the source for the recolonization of at least some parts of the western Palearctic45,46.
With regard to the taxonomic debate surrounding N. f. niethammeri, the phylogenetic analyses performed here, using mitochondrial and intron sequences, indicate that N. f. niethammeri has not accumulated measurable genetic divergence with respect to N. f. fodiens. There is also no significant genetic differentiation between them, meaning that also allele frequencies are similar. Taking all this information into account, it is clear that N. f. niethammeri cannot be considered an independent species, contradicting previous studies where it was suggested that N. f. niethammeri might warrant species status11,15,18,19. An alternative suggestion is that N. f. niethammeri is an ecotype, although further work would be required to corroborate this point.
Indeed, the lack of genetic divergence and differentiation revealed here suggests that the large skull of N. f. niethammeri possibly arose as an adaptation to the environment. Two main hypotheses can be used to explain this. Firstly, a previous hypothesis proposed that more calcareous substrates present in the central part of the Cantabrian Range could have resulted in rivers richer in nutrients and a consequent selection of individuals with better-developed mandibles to capture larger prey17,18. However, N. fodiens lives in other areas with calcareous substrates where it displays no change in body size, so this is unlikely to have been the sole driver. Alternatively, the size increase of N. f. niethammeri could have resulted from ecological displacement due to competition with the Iberian endemic N. anomalus, similar to that observed in other mammals47,48. An increase in the size of N. f. niethammeri could have favored access to new resources, for example larger prey, thus limiting competition with N. anomalus. In principle, both species occupy the same aquatic habitat in the northern Iberian Peninsula and most of the range of N. f. niethammeri overlaps with that of N. anomalus12,21, making competition between the two species possible. The interaction of N. fodiens with N. milleri has been studied in Europe, where both species live sympatrically49. However, the interaction of N. fodiens with N. anomalus when they live sympatrically has never before been studied, and this may be totally different to that which occurs when it coincides with N. milleri, so we do not know if and how this interaction could have stimulated a size increase in N. f. niethammeri. We therefore suggest that future studies be directed at understanding the micro-habitat and inter-specific interactions of these Neomys species. We hope that a combined genetic and ecological approach will help unravel why N. f. niethammeri experienced an abrupt increase in skull size across a narrow strip in the Iberian Peninsula, and reveal the evolutionary advantages and possible ecological consequences of this phenotypic novelty.
A total of 79 samples from the Palearctic range of the genus Neomys, with special emphasis on N. f. niethammeri and N. f. fodiens from the Iberian Peninsula, were analyzed (Fig. 1 and Supplementary Table S1). These included 68 skull samples from barn owl pellets collected in the field, of which 65 could be used for genetics and morphometry, and 3 could only be used for genetic analysis. Some of these samples had been analyzed in a previous morphological study of N. f. niethammeri17. In addition, 9 tissue samples were loaned from museums and colleagues, and 2 tissue samples were taken from our own collection.
To complete the phylogenetic analysis, cytochrome b and nuclear sequences of 18 Neomys samples were taken from Igea et al.13 and 39 cytochrome b sequences were downloaded from GenBank50. Two of the N. fodiens skull samples available from Igea et al.13 were used for morphometry.
No live animals were collected for this study and therefore no ethics permit was necessary.
Measurements and geometric morphometric analysis
After cleaning the skulls extracted from the owl pellets, we used only one lower mandible per skull and the rest was stored. Images of the 67 mandibles, together with a scale, were taken with a Canon 100D camera and a Canon EF-S 60 mm f/2.8 macro objective. The ImageJ 1.50i51 program was then utilized to take 16 landmarks from each sample (Supplementary Fig. S2 and Supplementary Table S2). Many of the mandibles were partially broken or without teeth due to the digestion process so that no landmarks were taken in teeth. Landmarks 1 and 7 were used to calculate the coronoid height (for six partial mandibles, only these two landmarks could be obtained). According to previous works, the coronoid height ranges considered to discriminate the different taxa were: ≤4.70 mm for N. anomalus; 4.80–5.35 mm for N. f. fodiens; and >5.35 mm for N. f. niethammeri19,23. With the coordinates of the 16 landmarks, and using MorphoJ version 1.06d52, we made a Procrustes fit, calculated the centroid size, and performed a principal components analysis from the covariance matrix. Landmark coordinates of the mandibles used in this study are available in TPS format in Supplementary Appendix 1.
DNA extraction, PCR amplification and sequencing
The photographed mandibles were then used for DNA extraction. They were first powdered using liquid nitrogen and a mortar after which genomic DNA was extracted with a QIAamp DNA Micro kit. In the case of tissues, DNA was extracted with a DNeasy Blood & Tissue Kit (QIAGEN) following the recommended protocol. Extractions of all degraded samples were performed in a separate room with UV irradiation to avoid contamination. Extraction blanks were always present in order to detect any possible contamination at each step. Additionally, pre-PCR procedures were developed in a dedicated UV-hood, in a controlled, sterile room.
Complete cytochrome b sequences (1140 bp) from N. fodiens samples were amplified in three fragments using already published primers13 with slight modifications to improve amplification (Supplementary Table S3). In addition, primers for a smaller fragment of 226 bp were developed with the purpose of amplifying DNA from the most degraded samples (Supplementary Table S3). The length amplified in each sample is shown in Supplementary Table S1.
For the nuclear markers, a set of six new primer pairs were designed starting from intron markers previously developed for Neomys13. The primers were placed in conserved intronic regions or exons that spanned small fragments (between 153 and 229 bp) and flanked the highest possible number of polymorphic sites. Some markers were amplified with more than one primer pair in various samples, as we reduced the amplified intron length during the work to enable the amplification of degraded samples that failed with the initial primers (Supplementary Table S4). PCR reactions were performed in a final volume of 25 µl with 2–6 µl genomic DNA, 0.15 µl of Promega GoTaq DNA polymerase, and 1 µM of each primer. The cycling conditions included an initial denaturation step of 30 s at 95 °C, followed by 40 cycles of denaturation (30 s at 95 °C), annealing (60 s at 54 °C for cytochrome b and 65 °C for introns), and extension (60 s at 72 °C), as well as a final extension of 5 min at 72 °C. For the most degraded skull samples, an alternative protocol using the QIAGEN Multiplex PCR was performed in a final volume of 50 µl with 4 µl of genomic DNA, 0.3 µM of each primer, and 25 µl of PCR Master Mix. In this case, there was an initial heat activation step of 15 min at 95 °C, the denaturation step was at 94 °C, the annealing temperature was lowered to 63 °C for the introns, and the annealing time was extended to 90 s. PCR products were purified using ExoSAP-It (Affymetrix) and sequenced at Macrogen Inc. Sequences were assembled using Geneious Pro 5.1.7 (https://www.geneious.com).
In introns where two or more variable sites were present in a sample, PHASE version 2.1.153 with a threshold of 0.9 was used to phase the alleles. When the program did not produce results or length-heterozygous alleles were present, allele-specific primers were used to independently amplify the two alleles. Allele-specific primers consist of two primers that are identical to one another except for the last nucleotide, which is situated over a polymorphic position of the sequence to be phased. The use of this type of primers was suggested for the sequencing reaction54, although in this work we used them both for amplifying and sequencing. To design them, a polymorphic position was selected and two 19–20 nucleotide primers were synthetized, each of which had one of the two possible nucleotides placed at the 3′ end. Then, two independent PCR reactions were performed, one for each allele-specific primer, and using the opposite original primer at the other side of the polymorphic region for amplification. In this way, two PCR products, corresponding to the two alleles, were obtained. Finally, each PCR product was sequenced with the corresponding allele-specific primer to obtain the resolved partial allele, which was then assembled with the original PCR sequence to obtain the complete allele54. The primers used for PCR allele-specific resolution are shown in Supplementary Table S5.
Phylogenetic analyses of cytochrome b
Since some cytochrome b sequences were completely amplified whereas others were only partial (Supplementary Table S1), they were aligned using MAFFT version 7.13055 with the maxiterate option enabled.
A Bayesian tree of the cytochrome b sequences was built using BEAST version 2.5.056. To select a statistically appropriate model, a Bayes factors approach based on path sampling57 was used with 96 complete sequences. Markov chain Monte Carlo analyses were based on 100 steps of 10,000,000 generations sampled each 1,000 generations, 10% preburn-in, 10% burn-in, and an alpha parameter of the Beta distribution to divide steps of 0.3. The convergence of each tree was checked in Tracer v1.7.1, from the same software package. Different priors were tested for each parameter category, and a more complex model was selected only if it converged and improved the log marginal likelihood by more than 5, as recommended57. Using these criteria, the selected model was the following: HKY substitution model with estimated base frequencies and Gamma site heterogeneity for each partition (unlinked substitution models); a strict clock model for all partitions (linked clock model); and a coalescent constant size tree model. Once the best model had been selected, it was applied to the sequences of either all Neomys species or only N. fodiens. In these cases, 50,000,000 generations were run. Consensus trees were calculated using the TreeAnnotator program (BEAST2 package) with median heights.
For comparison, a maximum-likelihood tree of all sequences was reconstructed with RAxML version 8.0.1958 using a GTR substitution model (as recommended in the manual of this program), rate heterogeneity modeled with a Gamma distribution, and 100 randomized maximum-parsimony starting trees. Mid-point rooting was used to represent the tree.
The Neomys alleles showed some differences in length due to small indels. They were aligned with MAFFT version 7.13055 with the maxiterate option enabled. Then, a few gap positions as well as a few positions with unknown nucleotides were removed from each alignment. The six final alignments are available in FASTA format in Supplementary Appendix S2.
In addition, we reconstructed a phylogenetic distance tree from the intron alignments, as in Igea et al.13. First, pairwise distances were calculated in such a way that the two alleles of each sequence were taken into account by making all possible comparisons between alleles60, and correcting for multiple substitutions using the Jukes-Cantor formula. The pairwise distance matrix was then utilized to construct a tree with the Fitch program of the Phylip software package61. Mid-point rooting was used to represent the tree.
Intron alignments were converted to a diploid multi-allelic data format by assigning a number to each allele. Then, pairwise FST for all populations was calculated with the R package hierfstat version 0.04–2262 using the genet.dist function with the WC84 method. Significance of the observed FST values was estimated by bootstrapping over loci using the boot.ppfst function of the same package with 100,000 replications and calculating the 95% confidence intervals. Significance was inferred if the confidence interval did not overlap zero.
Nuclear genetic diversity (π and θ) was calculated using the Bioperl library PopGen version 1.692463. The number of heterozygous positions in each sample were counted across the different nuclear markers and divided by their respective lengths. A map of heterozygosity values was then represented with QGIS64.
A total of 611 new sequences were deposited in EMBL/GenBank with Accession Numbers LR585354-LR585964, using the European Nucleotide Archive. For introns amplified using various primer pairs, only the shortest sequence was deposited for all samples.
Papadopoulou, A. & Knowles, L. L. Toward a paradigm shift in comparative phylogeography driven by trait-based hypotheses. Proc. Natl Acad. Sci. USA 113, 8018–8024 (2016).
Zamudio, K. R., Bell, R. C. & Mason, N. A. Phenotypes in phylogeography: Species’ traits, environmental variation, and vertebrate diversification. Proc. Natl Acad. Sci. USA 113, 8041–8048 (2016).
McNab, B. K. Geographic and temporal correlations of mammalian size reconsidered: a resource rule. Oecologia 164, 13–23 (2010).
Yom-Tov, Y. & Geffen, E. Recent spatial and temporal changes in body size of terrestrial vertebrates: probable causes and pitfalls. Biol. Rev. 86, 531–541 (2011).
Ashton, K. G., Tracy, M. C. & de Queiroz, A. Is Bergmann’s Rule Valid for Mammals? Am. Nat. 156, 390–415 (2000).
Lomolino, M. V., Sax, D. F., Palombo, M. R. & Van Der Geer, A. A. Of mice and mammoths: evaluations of causal explanations for body size evolution in insular mammals. J. Biogeogr. 39, 842–854 (2012).
Martinez, P. A. et al. The contribution of neutral evolution and adaptive processes in driving phenotypic divergence in a model mammalian species, the Andean fox Lycalopex culpaeus. J. Biogeogr. 45, 1114–1125 (2018).
Paetkau, D., Shields, G. F. & Strobeck, C. Gene flow between insular, coastal and interior populations of brown bears in Alaska. Mol. Ecol. 7, 1283–1292 (1998).
Shafer, A. B. A., Nielsen, S. E., Northrup, J. M. & Stenhouse, G. B. Linking genotype, ecotype, and phenotype in an intensively managed large carnivore. Evol. Appl. 7, 301–312 (2014).
Docampo, M., Moreno, S. & Santoro, S. Marked reduction in body size of a wood mouse population in less than 30 years. Mamm. Biol. 95, 127–134 (2019).
Burgin, C. J., et al. Species accounts of Soricidae. In Handbook of the Mammals of the World. Volume 8. Insectivores, Sloths and Colugos (eds. Mittermeier, R. A. & Wilson, D. E.) (Lynx Edicions, 2018).
Ventura, J. Neomys fodiens (Pennant, 1771). In Atlas y libro rojo de los mamíferos terrestres de España (eds. Palomo, J., Gisbert, J. & Blanco, J. C.) 111–113 (Dirección General para la Biodiversidad-SECEM-SECEMU, 2007).
Igea, J., Aymerich, P., Bannikova, A. A., Gosálbez, J. & Castresana, J. Multilocus species trees and species delimitation in a temporal context: application to the water shrews of the genus Neomys. BMC Evol. Biol. 15, 209 (2015).
Mendes-Soares, H. & Rychlik, L. Differences in swimming and diving abilities between two sympatric species of water shrews: Neomys anomalus and N. fodiens (Soricidae). J. Ethol. 27, 317–325 (2009).
Wilson, D. E. & Reeder, D. M. Mammal species of the world. A taxonomic and geographic reference. (Johns Hopkins University Press, 2005).
Bühler, P. Neomys fodiens niethammeri ssp. n., eine neue Wasserspitzmausform aus Nord-Spanien. Bonn zool. Beitr. 14, 165–170 (1963).
Nores, C., Canals, J. S., Castro, A. D. & Gonzalez, G. Variation du genre Neomys Kaup, 1829 (Mammalia, Insectivora) dans le secteur cantabro-galicien de la péninsule Ibérique. Mammalia 46, 361–373 (1982).
López-Fuster, M. J., Ventura, J., Miralles, M. & Castién, E. Craniometrical characteristics of Neomys fodiens (Pennant, 1771) (Mammalia, Insectivora) from the northeastern Iberian Peninsula. Acta Theriol. 35, 269–276 (1990).
Bühler, P. Zum taxonomischen Status der Großkopf-Wasserspitzmaus (Neomys fodiens niethammeri Bühler, 1963), aus Spanien nebst Festlegung und Beschreibung eines Neotypus. Bonn zool. Beitr. 46, 307–314 (1996).
Kryštufek, B. & Quadracci, A. Effects of latitude and allopatry on body size variation in European water shrews. Acta Theriol. 53, 39–46 (2008).
Ventura, J. Neomys anomalus Cabrera, 1907. in Atlas y libro rojo de los mamíferos terrestres de España (eds. Palomo, J., Gisbert, J. & Blanco, J. C.) 114–116 (Dirección General para la Biodiversidad-SECEM-SECEMU, 2007).
Querejeta, M. & Castresana, J. Evolutionary history of the endemic water shrew Neomys anomalus: Recurrent phylogeographic patterns in semi-aquatic mammals of the Iberian Peninsula. Evol. Ecol. 8, 10138–10146 (2018).
Blanco, J. C. Mamíferos de España. Vol 1. Insectívoros, Quirópteros, Primates y Carnívoros de la Península Ibérica, Baleares y Canarias. (GeoPlaneta, 1998).
Cuenca-Bescós, G., Straus, L. G., González Morales, M. R. & García-Pimienta, J. C. Paleoclima y paisaje del final del Cuaternario en Cantabria: Los pequeños mamíferos de la cueva del Mirón (Ramales de la Victoria). Revista Española de Paleontología 23, 91–126 (2008).
Sesé, C. Los micromamíferos (Eulipotyphla, Chiroptera, Rodentia y Lagomorpha) del yacimiento del Pleistoceno Superior de la cueva de El Castillo (Cantabria, España). Estudios Geológicos 73, e072 (2017).
Rohland, N. & Hofreiter, M. Comparison and optimization of ancient DNA extraction. BioTechniques 42, 343–352 (2007).
Carroll, E. L. et al. Genetic and genomic monitoring with minimally invasive sampling methods. Evol. Appl. 11, 1094–1119 (2018).
Waits, L. P. & Paetkau, D. Noninvasive genetic sampling tools for wildlife biologists a review of applications and recommendations for accurate data collection. J. Wildl. Manage. 1418–1433 (2005).
McCarthy, M. S. et al. Genetic censusing identifies an unexpectedly sizeable population of an endangered large mammal in a fragmented forest landscape. BMC Ecol. 15, 21 (2015).
Taberlet, P. & Fumagalli, L. Owl pellets as a source of DNA for genetic studies of small mammals. Mol. Ecol. 5, 301–305 (1996).
Poulakakis, N., Lymberakis, P., Paragamian, K. & Mylonas, M. Isolation and amplification of shrew DNA from barn owl pellets. Biol. J. Linn. Soc. 85, 331–340 (2005).
Barbosa, S., Pauperio, J., Searle, J. B. & Alves, P. C. Genetic identification of Iberian rodent species using both mitochondrial and nuclear loci: application to noninvasive sampling. Mol. Ecol. Resour. 13, 43–56 (2013).
Hailer, F. et al. Nuclear genomic sequences reveal that polar bears are an old and distinct bear lineage. Science 336, 344–347 (2012).
Toews, D. P. L. & Brelsford, A. The biogeography of mitochondrial and nuclear discordance in animals. Mol. Ecol. 21, 3907–3930 (2012).
Brito, P. H. & Edwards, S. V. Multilocus phylogeography and phylogenetics using sequence-based markers. Genetica 135, 439–455 (2009).
Sánchez-Gracia, A. & Castresana, J. Impact of deep coalescence on the reliability of species tree inference from different types of DNA markers in mammals. PLOS ONE 7, e30239 (2012).
Igea, J., Juste, J. & Castresana, J. Novel intron markers to study the phylogeny of closely related mammalian species. BMC Evol. Biol. 10, 369 (2010).
Kearns, A. M. et al. Nuclear introns help unravel the diversification history of the Australo-Pacific Petroica robins. Mol. Phylogenet. Evol. 131, 48–54 (2019).
Degnan, J. H. & Rosenberg, N. A. Gene tree discordance, phylogenetic inference and the multispecies coalescent. Trends Ecol. Evol. 24, 332–340 (2009).
Knowles, L. L. The burgeoning field of statistical phylogeography. J. Evol. Biol. 17, 1–10 (2004).
Omland, K. E., Baker, J. M. & Peters, J. L. Genetic signatures of intermediate divergence: population history of Old and New World Holarctic ravens (Corvus corax). Mol. Ecol. 15, 795–808 (2006).
Stewart, J. R., Lister, A. M., Barnes, I. & Dalén, L. Refugia revisited: individualistic responses of species in space and time. Proc. R. Soc. B 277, 661–671 (2010).
Schmitt, T. & Varga, Z. Extra-Mediterranean refugia: The rule and not the exception? Front. Zool. 9, 22 (2012).
López-García, J. M. et al. Palaeoenvironmental and palaeoclimatic reconstruction of the Latest Pleistocene of El Portalón Site, Sierra de Atapuerca, northwestern Spain. Palaeogeogr. Palaeoclimatol. Palaeoecol. 292, 453–464 (2010).
Hewitt, G. M. Post-glacial re-colonization of European biota. Biol. J. Linn. Soc. 68, 87–112 (1999).
Schmitt, T. Molecular biogeography of Europe: Pleistocene cycles and postglacial trends. Front. Zool. 4, 11 (2007).
Hulva, P., Horácek, I., Strelkov, P. P. & Benda, P. Molecular architecture of Pipistrellus pipistrellus/Pipistrellus pygmaeus complex (Chiroptera: Vespertilionidae): further cryptic species and Mediterranean origin of the divergence. Mol. Phylogenet. Evol. 32, 1023–1035 (2004).
Biedma, L., Román, J., Calzada, J., Friis, G. & Godoy, J. A. Phylogeography of Crocidura suaveolens (Mammalia: Soricidae) in Iberia has been shaped by competitive exclusion by C. russula. Biol. J. Linn. Soc. 1–15 (2018).
Rychlik, L. & Zwolak, R. Interspecific aggression and behavioural dominance among four sympatric species of shrews. Can. J. Zool. 84, 434–448 (2006).
Clark, K., Karsch-Mizrachi, I., Lipman, D. J., Ostell, J. & Sayers, E. W. GenBank. Nucleic Acids Res. 44, D67–72 (2016).
Schneider, C. A., Rasband, W. S. & Eliceiri, K. W. NIH Image to ImageJ: 25 years of image analysis. Nat. Methods 9, 671–675 (2012).
Klingenberg, C. P. MorphoJ: an integrated software package for geometric morphometrics. Mol. Ecol. Resour. 11, 353–357 (2011).
Stephens, M., Smith, N. J. & Donnelly, P. A new statistical method for haplotype reconstruction from population data. Am. J. Hum. Genet. 68, 978–989 (2001).
Scheen, A.-C. et al. Use of allele-specific sequencing primers is an efficient alternative to PCR subcloning of low-copy nuclear genes. Mol. Ecol. Resour. 12, 128–135 (2012).
Katoh, K. & Standley, D. M. MAFFT multiple sequence alignment software version 7: improvements in performance and usability. Mol. Biol. Evol. 30, 772–780 (2013).
Bouckaert, R. et al. BEAST 2: a software platform for Bayesian evolutionary analysis. PLoS Comp. Biol. 10, e1003537 (2014).
Baele, G. et al. Improving the accuracy of demographic and molecular clock model comparison while accommodating phylogenetic uncertainty. Mol. Biol. Evol. 29, 2157–2167 (2012).
Stamatakis, A. RAxML version 8: a tool for phylogenetic analysis and post-analysis of large phylogenies. Bioinformatics 30, 1312–1313 (2014).
Salzburger, W., Ewing, G. B. & Haeseler von, A. The performance of phylogenetic algorithms in estimating haplotype genealogies with migration. Mol. Ecol. 20, 1952–1963 (2011).
Freedman, A. H. et al. Genome sequencing highlights the dynamic early history of dogs. PLOS Genet. 10, e1004016 (2014).
Felsenstein, J. PHYLIP-phylogeny inference package (version 3.4). Cladistics 5, 164–166 (1989).
Goudet, J. HIERFSTAT, a package for R to compute and test hierarchical F-statistics. Molecular Ecology Notes 5, 184–186 (2005).
Stajich, J. E. & Hahn, M. W. Disentangling the effects of demography and selection in human history. Mol. Biol. Evol. 22, 63–73 (2005).
QGIS Development Team. QGIS Geographic Information System. Open Source Geospatial Foundation Project, http://qgis.osgeo.org (2019).
We thank the Museum of Southwestern Biology, the University of Alaska Museum, Adrián Álvarez Vena, Anna Bannikova and Juan Fernández Gil for samples, and Alfonso Balmori Martínez for help with field work and discussions. We also thank Link E. Olson and an anonymous reviewer for their helpful comments on this manuscript. This work was financially supported by research projects CGL2014-53968-P and CGL2017-84799-P of the “Plan Nacional I + D + I del Ministerio de Ciencia, Innovación y Universidades (Spain)”, cofinanced with FEDER funds (AEI/FEDER, UE), to J.C. Support was also provided by grant 2017-SGR-991 of the “Generalitat de Catalunya”. A.B.P. was supported by research contract BES-2015-074119 of the “Ministerio de Ciencia, Innovación y Universidades”, cofinanced with FEDER funds.
The authors declare no competing interests.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Balmori-de la Puente, A., Nores, C., Román, J. et al. Size increase without genetic divergence in the Eurasian water shrew Neomys fodiens. Sci Rep 9, 17375 (2019). https://doi.org/10.1038/s41598-019-53891-y
Environmental context for the Late Pleistocene (MIS 3) transition from Neanderthals to early Modern Humans: Analysis of small mammals from La Güelga Cave, Asturias, northern Spain
Palaeogeography, Palaeoclimatology, Palaeoecology (2020)