Variation and population structure play key roles in the speciation process, but adaptive intraspecific genetic variation is commonly ignored when forecasting species niches. Amphibians serve as excellent models for testing how climate and local adaptations shape species distributions due to physiological and dispersal constraints and long generational times. In this study, we analysed the climatic factors driving the evolution of the genus Alytes at inter- and intraspecific levels that may limit realized niches. We tested for both differences among the five recognized species and among intraspecific clades for three of the species (Alytes obstetricans, A. cisternasii, and A. dickhilleni). We employed ecological niche models with an ordination approach to perform niche overlap analyses and test hypotheses of niche conservatism or divergence. Our results showed strong differences in the environmental variables affecting species climatic requirements. At the interspecific level, tests of equivalence and similarity revealed that sister species were non-identical in their environmental niches, although they neither were entirely dissimilar. This pattern was also consistent at the intraspecific level, with the exception of A. cisternasii, whose clades appeared to have experienced a lower degree of niche divergence than clades of the other species. In conclusion, our results support that Alytes toads, examined at both the intra- and interspecific levels, tend to occupy similar, if not identical, climatic environments.
Climatic factors may act as ecological barriers that can determine the distribution of animal and plant species1. This may explain why incipient speciation processes often can be inferred from the analysis of patterns of niche divergence2. Genetic variation, species spatial structure resulting from landscape barriers to gene flow, and intraspecific evolutionary processes (e.g., local adaptation) are the major drivers of speciation. Therefore, it is not surprising that genetic studies combined with ecological niche models have been proven to be powerful tools to study evolutionary processes and resolve biodiversity conservation problems3. In addition, the characterization of environmental niches is essential to understanding species distributions and patterns of biological diversity. Correlative ecological niche modelling33 is a common tool used to approach this characterization3. However, is the species level the most adequate level for this approach? Smith et al.4 suggest that we must consider local adaptations as evolutionary factors affecting niche requirements, and therefore, inclusion of evolutionary relationships below and above the species level should be considered. For this reason, it is informative to compare niche modes across taxa in a separate way, considering species and local genetic lineages. Amongst vertebrates, amphibians are ideal organisms to analyse this question because their physiology is highly constrained by environmental factors5,55, and they have low dispersal abilities. This combination of characteristics is expected to promote the evolution of local adaptations to match the spatial complexity of environmental variation7.
It is well known that vicariant events can drive divergence by limiting genetic exchange among evolutionary units8, but currently, there is evidence that environmental factors can also play a key role in biological diversification9,10,11. Although habitat suitability models and niche similarity comparisons have been previously conducted at interspecific and intraspecific levels for the midwife toads (Alytes sp.), these models have been implemented only in A. obstetricans9. However, other Mediterranean species, such as A. cisternasii and A. dickhilleni, have not been studied using nested models (inter- and intraspecific climatic niche divergence schemes) despite the fact that their genetic and phylogenetic discontinuities are well documented12,13. Furthermore, an interspecific perspective of climatic niches for all the species in the genus is crucial for a better understanding of climatic determinants and the differentiation processes involved.
Recent studies on niche modelling have shown that environmental conditions can drive evolution across geographical ranges and affect patterns of genetic structure14,9,15. Moreover, genetic isolation and local adaptation can synergistically influence the fate of species16, and biogeographic and vicariant events can drive species differentiation (see Martínez-Solano et al.17). However, the environmental factors involved in the maintenance of the current differenciation of species and evolutionary units have not been tested as a whole. Tectonic factors, with the formation of a mountain range in the Gibraltar Strait during the Upper Tortonian stage, played an important role in the speciation of the genus Alytes 18,17. In fact, the geographic isolation of A. muletensis and A. maurus might have strongly affected their environmental niches. Finally, recent work suggests that a more complex geological scenario might have affected the evolutionary history of Alytes in its southern range, with a Pliocene volcanic archipelago between Cabo de Gata and the eastern Rif coast19.
The major aims of this study were (1) to characterize the realized niche differences and environmental factors that promote the differentiation and the observed distribution of Alytes species, and (2) to investigate the importance of niche evolution by testing the hypotheses niche conservatism, as the maintenance of ancestral requirements among species with a common ancestor20, and niche divergence, as the appearance of divergences among these species2. Additionally, we tested whether the observed patterns of niche environmental evolution were consistent at two phylogenetic scales: interspecific and intraspecific (i.e., genetic lineages from Dias et al.12; Gonçalves et al.13; and Maia-Carvalho et al.9). We assumed the existence of differentiation at both inter- and intraspecific levels as a consequence of climatic niche differentiation. In this scheme, intra- and interspecific differentiation may be influenced by climate and geographic barriers throughout genetic variation and structure. Finally, We also aimed to determine whether the processes of niche and phylogenetic evolution were parallel by predicting whether subclades would show a phylogenetic signal.
Organism presence records and environmental data
The genus Alytes Wagler 1829 currently contains five living species. Alytes obstetricans (Laurenti, 1768) has the broadest geographical range of all the species in this group. Alytes cisternasii Boscá 1879 is endemic to the south-western region of the Iberian Peninsula. Alytes muletensis (Sanchiz & Adrover 1979) has a narrower distributional range and is endemic to the northern part of Mallorca Island. Alytes (Baleaphryne) dickhilleni Arntzen & García-París 1995 is endemic to the Betic Region on the south-eastern Iberian Peninsula. Finally, Alytes maurus Pasteur & Bons 1962, is a species distributed in some regions of the Rif and Middle Atlas of Morocco. Additionally, four recognized subspecies of A. obstetricans have been described: A. o. almogavarii Arntzen & García-París, 1995, from southern France to the Ebro River; A. o. obstetricans (Laurenti 1768), from Western Europe to north of the Iberian Peninsula; A. o. boscai Lataste 1879, in central and northern Portugal; and finally A. o. pertinax García-París & Martínez-Solano, 2001, on the eastern Iberian Peninsula.
The habitats of these five species show a large degree of differentiation. A. obstetricans requires areas with high amounts of precipitation and occupy a wide range of habitats, from mountain ranges to crops21. A. muletensis is only known in a few localities on northern Mallorca Island22, whereas A. maurus is restricted to a few localities in the Rif and Middle Atlas Mountains of Morocco and typically occupies humid sites in karst and steep areas23. Regarding the two Iberian endemics, A. dickhilleni is restricted to the Betic region in southeastern Spain24. A. cisternasii occupies the central-south-western sector of the Iberian Peninsula, usually between 0 and 700 m25, and, in comparison to the other species of this genus, it is associated with a hotter and drier climate26.
We used 676 localities to build ecological niche models. A total of 319 A. dickhilleni presence points were surveyed by the authors within all their Andalusian distribution areas. We identified 170 local population locations of A. cisternasii (including our own collection data and data from Amphibiaweb27), 162 of A. obstetricans (our data, Amphibiaweb, and in addition, revised data from www.observation.org), 14 of A. maurus (our data, Amphibiaweb and Donaire et al.23), and 11 of A. muletensis (our data and Amphibiaweb). All populations were separated by at least 200 m. Figure 1 shows the distribution of points selected for all five species.
To establish intraspecific comparisons among A. cisternasii, A. dickhilleni and A. obstetricans, we used presence data for the genetic lineages reported for these species. Presence data were assigned to lineages according to Gonçalves et al. (A. cisternasii)13, Dias et al. (A. dickhilleni)12, and Maia-Carvalho et al. (A. obstetricans)9 (the central-eastern lineage of A. obstetricans was excluded because of the low number of presence points). Some local populations could not be assigned to any of the reported lineages, as these locations are in contact zones our outside the areas surveyed in the cited studies, and therefore, these were removed from the data set. We excluded 42 locations of A. dickhilleni and 6 of A. cisternasii. For the geographically restricted A. muletensis and A. maurus, the low number of records and lack of adequate genetic lineage information precluded intraspecific analysis. Even in a well-designed data survey across all of the range of a species, model outputs are sensitive to sampling bias28. To reduce this bias, we used a sub-sample representing 25% of the populations of each species and lineages included in the study (random selection by MaxEnt). In addition, intraspecific figures show the presence points that were selected for each lineage and then used in the intraspecific correlative model.
We considered climatic and topographic factors to explain the realized distributions and niches of the five Alytes species. Climatic variables were obtained from WorldClim version 2 database at 30 s29, and topographic data were obtained from SRTM (https://www2.jpl.nasa.gov/srtm/dataprelimdescriptions.html). The study area was fixed to the distribution limits of the Alytes sp. Genus, and in order to avoid a high correlation and redundancy among the predictors, we performed pairwise Pearson correlations, and for r > 0.6, the variable with lower biological relevance was excluded. The final data set included five climatic variables: mean diurnal range, isothermality, minimum temperature of the coldest month, mean temperature of the driest quarter, and precipitation of the wettest month.
Niche model analyses
We performed two different modelling approaches: ecological niche models (ENMs) and an ordination technique30. First, of the different ENMs types, we selected the widely used machine learning method MaxEnt (version 3.4.1) to build the SDMs 31. The model was fitted using hinge, product, linear, and quadratic features with a maximum of 10,000 background points, 1,000 replicates, and clamping. Models were fitted by using the area under the ROC curve (AUC and ROC represents “receiver operating characteristic”31). We used the Cloglog output format. Although this measure has been extensively used to fit models, its usefulness has been criticized, especially for presence/background models such as MaxEnt. Thus, in addition to AUC, we present the values of its components, sensitivity and/or specificity32. To obtain these two indices, the continuous MaxEnt output was transformed into a categorical variable (predicted presence/absence). For this transformation, we applied the threshold of the minimum training presence (the lowest suitability scores associated with the populations of each lineage/species) given in the MaxEnt output sheet. We calculated the specificity from the confusion matrix33. This is a conservative and realistic threshold since it may include even small suitability scores whenever the lineages/species are present34. In this case, a calculation of sensitivity was not necessary since the applied threshold was fixed at the maximum. In addition, we have followed the Raes and Ter Steege validation method57, including 95% I.C AUC values of null models created with random points of the same size of the presences included in our models. ENM AUC values that are higher than their corresponding 95% CI AUC value of the fitted null model, significantly deviate from what would be expected by chance (p < 0.05).
The ordination technique approach was applied to perform niche overlap analyses, either between pairs of the five species or between pairs of the lineages within A. cisternasii, A. dickhilleni and A. obstetricans. We used the tool Ecospat, which incorporates null hypotheses35. For these analyses, we performed the following tests: niche equivalency tests (are niches identical?), similarity tests (are niches more similar than expected by chance?), and niche principal component analysis (PCA). As a measurement of the realized niche overlap, we calculated a Schoener’s D index through the niche-PCA. This index ranges from 0 to 1 to reflect no overlap to total overlap, respectively 36. For both the niche equivalency and similarity tests, we used the argument = ”greater” (overlap greater than expected by chance) to test the conservatism hypothesis and the argument = ”lower” (overlap lower than expected by chance) to test the divergence hypothesis35. We performed 1,000 permutations for each analysis. Additionally, we integrated phylogenies (inter- and intraspecific levels) using the age-range correlation function of the Phyloclim package38. This function is used to test for phylogenetic signals in patterns of niche overlap. Slopes and intercepts derived from a linear model can be used to characterize speciation mode (allopatric versus sympatric) or niche evolution (conservatism versus flexibility) in the clade39.
Regarding the choice of the geographical extent (and as a consequence, environmental background), we used the software QGIS40 to compile and process environmental data using the extension point sampling tool41. Analyses were conducted using R42. The study area for the interspecific analysis with MaxEnt and ECOSPAT was adapted to the total distribution of the genus to allow comparisons. At the intraspecific level, we used the same area in each cluster of lineages (the species ranges).
At the interspecific level, the Maxent outputs are shown in Fig. 2. The variables with a relatively higher percentage of contribution in the Maxent models were isothermality (62.5%; A. obstetricans), mean temperature of the driest quarter (56.3%; A. cisternasii), mean temperature of the driest quarter (40.2%; A. dickhilleni), precipitation of the wettest month (90.4%; A. muletensis) and, finally, precipitation of the wettest month (73.8%; A. maurus). The AUC, 95% I.C. AUC of null model and specificity values were 0.90 ± 0.03, 0.86 and 0.65 (A. obstetricans); 0.92 ± 0.10, 0.84 and 0.40 (A. cisternasii); 0.94 ± 0.02, 0.90 and 0.67 (A. dickhilleni), 0.88 ± 0.16, 0.78 and 0.83 (A. muletensis), and 0.98 ± 11, 0.92 and 0.95 (A. maurus), respectively. The results of the niche overlap (Schoener’s D) and similarity and equivalency analyses are shown in Table 1. We found minimal niche overlap with significant p values for the equivalency test in the divergence hypothesis, except for the overlap between A. obstetricans and A. maurus. The magnitude and sign of the variables in the principal component plots of the niche are shown in Fig. 3.
Maxent outputs for intraspecific A. cisternasii, A. dickhilleni and A. obstetricans indicate differences in climatic suitability among lineages. The model outputs are shown in Fig. 4, and the ENM AUC, 95% I.C. AUC of fitted null models and specificity values are shown in Supplementary material 1. The variables with relatively higher contributions in each lineage of A. cisternasii were minimum temperature of the coldest month (66.2%) and isothermality (29.7%) for the western lineage, mean diurnal range (47.7%) and precipitation of the wettest month (24.1%) for the southern lineage, mean temperature of the driest quarter (52.3%), isothermality (24.3%) and mean diurnal range (23.4%) for the eastern lineage, and temperature of the driest quarter (45.9%) and mean diurnal range (31.5%) for the northern lineage. For A. dickhilleni, the most relevant variables were the mean temperature of the driest quarter (37.8%), precipitation of the wettest month (30%) and isothermality (26.3%) for the southern lineage; annual mean temperature (72.5%) for the northern lineage; precipitation of the wettest month (33.7%), annual mean temperature (29.9%) and isothermality (22.8%) for the western lineage; and annual mean temperature (50.1%) and temperature of the driest quarter (36.6%) for the eastern lineage. Finally, for A. obstetricans, the most relevant variables were precipitation of wettest month (90.9%) for the central-western lineage; precipitation of wettest month (36.9%) and annual mean temperature (24%) for the north-eastern lineage, precipitation of wettest month (60.5%) and annual mean temperature (26.7%) for the north-western lineage, mean diurnal range (63.9%) for the south-eastern lineage, and precipitation of wettest month for the south-western lineage.
The results of niche overlap (Schoener’s D) and similarity and equivalency analyses showed low to medium values depending on the pair of lineages compared and the species (see Table 2 for A. dickhilleni and A. cisternasii and Table 3 for A. obstetricans). The south-western lineage of A. dickhilleni has lower overlap values than those of the other lineages, and in the equivalency test, we obtained significant results for the divergence hypothesis compared with the niches of the other two lineages (equivalency test, divergence hypothesis, Table 2). There were no significant divergences or convergences between the niches of A. cisternasii lineages (Table 2). For A. obstetricans, we found significant values in the equivalency test between most lineage comparisons, but we also obtained several significant results for the niche conservatism hypothesis (Table 3). The magnitude and sign of variables in the principal component plots of the niche are provided in Fig. 5. We did not obtain any significance in the age-range correlation test, both at inter- and intraspecific levels (see Supplementary material 2, p values of 0.60 [interspecific], 0.28 [A. cisternasii], 0.98 [A. obstetricans], and 0.64 [A. dickhilleni]). In Supplementary material 2 we also provide cluster dendrograms based on niche overlap for both, intraspecific and interspecific levels.
Our results showed a clear spatial niche segregation when we examined interspecific niche variation in Alytes toads. On the Iberian Peninsula, the distribution outputs of the MaxEnt models fit neatly in some places, although they exhibited a slight overlap in certain areas that coincides with the present sympatric distributional area between A. cisternasii and A. obstetricans. The pattern derived from niche similarity and equivalence tests revealed that each Alytes species occupies a non-identical environmental niche since no significant p values were found for the hypothesis of complete niche overlap (equivalence test), but instead, highly significant distinctions occurred for the divergence hypothesis (equivalence test) for any pair-species comparisons with the exception of the A. obstetricans versus A. maurus contrast. This suggests an evolutionary scenario where niches are less equivalent (identical) than expected by chance in relation to different non-exclusive processes, including local adaptation. In addition, we did not find significant results in the similarity test (conservatism hypothesis), rejecting the hypothesis of retained similarity. We also did not find significance in the case of the divergence hypothesis for the similarity test, indicating no greater than expected divergence. However, rejecting the retained similarity, determining that the divergence was not greater than expected was already relatively divergent. A. cisternasii has been described as the most phylogenetically distant group within the genus Alytes17. This is compatible with an evolutionary scenario where the complex formed by A. obstetricans, A. maurus, A. muletensis, and A. dickhilleni share a more recent natural history and, consequently, they could also share similar environmental/climatic requirements to a high degree. However, our results did not support this prediction, thus suggesting that the niches of these species evolved in a complex scenario, creating a wide diversity of adaptations. A. maurus and A. obstericans presented the widest climatic range (see Fig. 2). In comparison to the other species (with the exception of A. maurus), A. obstetricans inhabits colder areas with higher precipitation. A. cisternasii occupies warmer areas with relatively high precipitation (at least in the wettest period); A. maurus faces a wider range of temperatures and a high rainfall amount but with the widest variable range. It is important to remark that our models shows two separate areas in the ecological niche models (Ecospat) of A.maurus, this being possibly this an artefact due to the lack of knowledge about the distribution or alternatively the isolation of the two extant populations56. In turn, in comparison to A. cisternasii and A. muletensis, A. dickhilleni is present in colder and drier areas. Finally, A. muletensis occupies warm and dry areas, although the distribution of this species was much wider in the past44; in addition, the current distribution may be restricted to highly isolated populations due to non-climatic factors such as intense predation pressure by the introduced water snake Natrix maura43. This scenario may bias the output of our correlative model, which relies on distributional and climatic factors. A process to determine the robustness of our approach could be to implement mechanistic physiologically based models and to examine the congruence of both approaches55.
When examining the degree of environmental niche evolution at the intraspecific level, we found contrasting patterns across and within species. The four clades of A. cisternasii tended to exhibit slight niche differentiation differences between the four genetically distinct clades, although correlative models showed different predicted distributions of the four lineages, with the western lineage being the most different, as it is associated with more humid conditions, than those the three other lineages that form a complex with reduced niche differentiation, in agreement with the phylogenetic tree proposed by Gonçalves et al.13. However, a contrasting pattern was found in A. dickhilleni, whose southern lineage exhibited significant non-equivalence with respect to the other three lineages, reflecting a more separated evolutionary history for this clade. Interestingly, this southern lineage differentiation in climatic requirements, characterized by a reduced diurnal range and mild winters (temperature of the coldest month) whereas the other three lineages exhibited differentiation in their climatic niches, fits well with the observed pattern of genetic divergence, by which the southern clade formed a sister group to a complex containing the other three lineages12. Finally, clades of the widespread Alytes obstetricans exhibited the highest diversity in the pattern of climatic niche evolution with high niche conservatism. The two southernmost lineages between the north-western and south-eastern lineages (in the similarity test) suggest a diminished importance of niche divergence for the intraspecific lineages described for this species. In addition, we did not find support for the existence of phylogenetic signals in the age-range correlation tests (both at interspecific and intraspecific levels). This allowed us to consider the flexibility in the niche evolution hypothesis as opposed to niche conservatism reported for other groups36.
Climatic conditions are important factors influencing both the inter- and intraspecific evolution of Alytes and consequently its ecological niche segregation. The evolutionary history of this genus seems to be the result of a combination of vicariant factors influenced by both landscape and geographic factors17. Our results for Alytes reinforce the idea that intraspecific variability can be one of the major drivers of biodiversity46. Our results also match the conclusions of Maia-Carvalho et al.9 about the ongoing processes of differentiation in A. obstetricans but provide a more general, wider view of the generation of diversity. Thus, vicariant and geographic barriers explain the current patterns (inter- and intraspecific) of diversification; environmental and geographical factors can act synergistically to drive differentiation at multiple scales. The intraspecific differences may be explained by the most commonly accepted evolutionary alternatives: (A) niche conservatism that may be the consequences of natural selection47. We observed a lower intraspecific niche divergence in A. cisternasii than in A. dickhilleni and, at the same time, a higher phylogenetic influence (p value lower). This may possibly be induced by its specialized thermophilic physiology that may constrain uplift dispersion to mountain ranges48 (Rodríguez-Rodríguez et al. unpublished data). B) Other selective sources affect relatively lower dispersal ability due to ecomorphological constraints. A. cisternasii is the shortest-limbed species in group 25, and indirectly, this may be associated with a lower dispersal ability than that of the other Alytes species49,50.
Regarding the phylogenetic analysis results, we conclude that no phylogenetic signal was detected at either interspecific or intraspecific levels. This fact is congruent with the conclusions the remaining tests that supported the rejection of retained niche similarity (conservatism), suggesting a nom parallelism of phylogenetic inertia and niche evolution.
Our results support a model of hierarchical niche differentiation in midwife toads. This model helps to understand the evolution of this primitive genus of amphibians, but most importantly, this approach has widespread application in conservation biology. First, it demonstrates the need for a modelling strategy based on targets below the species level. Second, it shows that the identification of a relatively reduced series of bioclimatic variables can enable the identification of the most sensitive taxa or lineages52. This emphasizes the importance of evolutionary distinctiveness53 and the need to connect species range projections with the concept of evolutionarily significant units (ESUs54) to prioritize conservation efforts.
The datasets generated during and/or analysed during the current study are available from the corresponding author upon reasonable request.
Janzen, D. H. Why mountain passes are higher in the tropics. Am. Nat. 101(919), 233–249 (1967).
Ackerly, D. D., Schwilk, D. W. & Webb, C. O. Niche evolution and adaptive radiation: Testing the order of trait divergence. Ecology 87(7), S50–S61 (2006).
Razgour, O. et al. Considering adaptive genetic variation in climate change vulnerability assessment reduces species range loss projections. Proc. Natl. Acad. Sci. 116(21), 10418–10423 (2019).
Smith, A. B., Godsoe, W., Rodríguez-Sánchez, F., Hsiao-Hsuan, W. & Warren, D. Niche estimation above and below the species level. Trends Ecol. Evol. https://doi.org/10.1016/j.tree.2018.10.012 (2018).
Bovo, R. P., Navas, C. A., Tejedo, M., Valença, S. E. & Gouveia, S. F. Ecophysiology of amphibians: Information for best mechanistic models. Diversity 10(4), 118 (2018).
Cushman, S. A. Effects of habitat loss and fragmentation on amphibians: A review and prospectus. Biol. Cons. 128(2), 231–240 (2006).
Sänem, K. R., Laurila, A. & Merilä, J. Geographic variation in acid stress tolerance of the moor frog Rana arvalis. I. Local adaptation. Evolution 57(2), 352–362 (2003).
Hewitt, G. M. Genetic consequences of climatic oscillations in the quaternary. Philos. Trans. R. Soc. Lond. B Biol. Sci. 359, 183–195 (2004).
Maia-Carvalho, B. et al. The roles of allopatric fragmentation and niche divergence in intraspecific lineage diversification in the common midwife toad (Alytes obstetricans). J. Biogeogr. 45(9), 2146–2158 (2018).
Alberdi, A. et al. Contrasting population-level responses to Pleistocene climatic oscillations in an alpine bat revealed by complete mitochondrial genomes and evolutionary history inference. J. Biogeogr. 42(9), 1689–1700 (2015).
Tocchio, L. J., Gurgel-Gonçalves, R., Escobar, L. E. & Peterson, A. T. Niche similarities among white-eared opossums (Mammalia, Didelphidae): Is ecological niche modelling relevant to setting species limits?. Zoolog. Scr. 44, 1–10 (2015).
Dias, G. et al. Limited gene flow and high genetic diversity in the threatened Betic midwife toad (Alytes dickhilleni): Evolutionary and conservation implications. Conserv. Genet. 16(2), 459–476 (2015).
Gonçalves, H. et al. High levels of population subdivision in a morphologically conserved Mediterranean toad (Alytes cisternasii) result from recent, multiple refugia: Evidence from mtDNA, microsatellites and nuclear genealogies. Mol. Ecol. 18, 5143–5160 (2009).
Antunes, B. et al. Combining phylogeography and landscape genetics to infer the evolutionary history of a short-range Mediterranean relict Salamandra salamandra longirostris. Conserv. Genet. 19(6), 1411–1424 (2018).
Tarroso, P., Pereira, R. J., Martínez-Freiría, F., Godinho, R. & Brito, J. C. Hybridization at an ecotone: Ecological and genetic barriers between three Iberian vipers. Mol. Ecol. 23, 1108–1123 (2014).
Lobo, A. et al. Local adaptation through genetic differentiation in highly fragmented Tilia cordata populations. Ecol. Evol. 8, 5968–5976 (2018).
Martínez-Solano, I., Gonçalves, H. A., Arntzen, J. W. & García-París, M. Phylogenetic relationships and biogeography of midwife toads (Discoglossidae: Alytes). J. Biogeogr. 31, 603–618 (2004).
Carranza, S., Arnold, E. N., Wade, E. & Fahd, S. Phylogeography of the false smooth snakes, Macroprotodon (Serpentes, Colubridae): mitochondrial DNA sequences show European populations arrived recently from Northwest Africa. Mol. Phylogenet. Evol. 33(3), 523–532 (2018).
Booth-Rea, G., Ranero, C. R. & Grevemeyer, I. The Alboran volcanic-arc modulated the Messinian faunal exchange and salinity crisis. Sci. Rep. 8(1), 13015 (2018).
Wellenreuther, M., Larson, K. W. & Svensson, E. I. Climatic niche divergence or conservatism? Environmental niches and range limits in ecologically similar damselflies. Ecology 93(6), 1353–1366 (2012).
Bosch, J. Sapo partero común -Alytes obstetricans. (eds. Salvador, A., Martínez-Solano, I.) Enciclopedia Virtual de los Vertebrados Españoles. (Museo Nacional de Ciencias Naturales, Madrid, 2014).
Oliver, J.A. Ferreret – Alytes muletensis. (eds. Salvador, A., Martínez-Solano, I.) Enciclopedia Virtual de los Vertebrados Españoles. (Museo Nacional de Ciencias Naturales, Madrid, 2014)
Donaire-Barroso, D., El Mouden, E. H., Slimani, T. & González de la Vega, J. P. On the meridional distribution of Alytes maurus Pasteur and Bons, 1962 (Amphibia, Discoglossidae). Herpetol. Bull. 96, 12 (2006).
Salvador, A. Sapo partero bético - Alytes dickhilleni. (eds. Salvador, A., Martínez-Solano, I.) Enciclopedia Virtual de los Vertebrados Españoles. https://www.vertebradosibericos.org/ (Museo Nacional de Ciencias Naturales, Madrid, 2015)
Márquez, R. Sapo partero ibérico -Alytes cisternasii. (eds. Salvador, A., Martínez-Solano, I.) Enciclopedia Virtual de los Vertebrados Españoles. https://www.vertebradosibericos.org/ (Museo Nacional de Ciencias Naturales, Madrid, 2017).
Márquez, R., Crespo, E.G. Alytes cisternasii. (eds. Pleguezuelos, J. M., Márquez, R., Lizana, M.) Atlas y Libro Rojo de los Anfibios y Reptiles de España. (Dirección General de Conservación de la Naturaleza- Asociación Herpetológica Española, Madrid, 2002).
Amphibiaweb.org. AmphibiaWeb. [online]. https://Amphibiaweb.org (2018).
Araujo, M. B. & Guisan, A. Five (or so) challenges for species distribution modelling. J. Biogeogr. 33(10), 1677–1688 (2006).
Fick, S., Hijmans, R. Bioclimatic variables/ WorldClim-Global Climate Data. [online] Worldclim.org. https://www.worldclim.org/bioclim (2018)
Guisan, A., Petitpierre, B., Broennimann, O., Daehler, C. & Kueffer, C. Unifying niche shift studies: insights from biological invasions. Trends Ecol. Evol. 29, 260–269 (2014).
Steven J. Phillips, Miroslav Dudík, Robert E. Schapire. [Internet] Maxent software for modeling species niches and distributions (version 3.4.1). https://biodiversityinformatics.amnh.org/open_source/maxent/.
Lobo, J. M., Jiménez-Valverde, A. & Real, R. AUC: a misleading measure of the performance of predictive distribution models. Glob. Ecol. Biogeogr. 17(2), 145–151 (2008).
Fielding, A. H. & Bell, J. F. A review of methods for the assessment of prediction errors in conservation presence/absence models. Environ. Conserv. 24, 38–49 (1997).
Fitze, P. S. et al. Integrative analyses of speciation and divergence in Psammodromus hispanicus (Squamata: Lacertidae). BMC Evol. Biol. 11, 347 (2011).
Di Cola, V. et al. Ecospat: an R package to support spatial analyses and modeling of species niches and distributions. Ecography 40(6), 774–787 (2017).
Warren, D. L., Glor, R. E. & Turelli, M. Environmental niche equivalency versus conservatism: quantitative approaches to niche evolution. Evol. Int. J. Organ. Evol. 62(11), 2868–2883 (2008).
Dufresnes, C., & Martínez-Solano, Í. (2019). Hybrid zone genomics supports candidate species in Iberian Alytes obstetricans. Amphibia-Reptilia, 1(aop), 1–8.
Heibl, C., Calenge, C. Integrating Phylogenetics and Climatic Niche Modeling (2018)
Fitzpatrick, B. M. & Turelli, M. The geography of mammalian speciation: mixed signals from phylogenies and range maps. Evolution 60, 601–615 (2006).
QGIS Development Team. QGIS Geographic Information System. Open Source Geospatial Foundation Project. https://qgis.osgeo.org (2018)
Jurgiel, B. Point Sampling Tool. QGIS Python Plugins Repository. https://plugins.qgis.org/plugins/pointsamplingtool/ (2018).
R Development Core Team. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. ISBN 3-900051-07-0. https://www.R-project.org. (2008)
Moore, R. D., Griffiths, R. A. & Román, A. Distribution of the Mallorcan midwife toad (Alytes muletensis) in relation to landscape topography and introduced predators. Biol. Cons. 116(3), 327–332 (2004).
Alcover, J.A., Mayol, D., Jaume, D., Alomar, G., Pomar, G., Jurado, J. Biología i ecología de les poblacions relictes de Baleaphryne muletensis a la muntaya mallorquina. (eds. Hemmer, H., Alcover, J.A.) Life History of the Mallorcan Midwife Toad. 129–152. (Editorial Moll, 1984).
Aragón, P., Baselga, A. & Lobo, J. M. Global estimation of invasion risk zones for the western corn rootworm Diabrotica virgifera virgifera: integrating distribution models and physiological thresholds to assess climatic favourability. J. Appl. Ecol. 47(5), 1026–1035 (2010).
Sánchez-Fernández, D., Aragón, P., Bilton, D. T. & Lobo, J. M. Assessing the congruence of thermal niche estimations derived from distribution and physiological data. A test using diving beetles. PLoS One 7(10), 48163 (2012).
Violle, C. et al. The return of the variance: intraspecific variability in community ecology. Trends Ecol. Evol. 27(4), 244–252 (2012).
Losos, J. B. Phylogenetic niche conservatism, phylogenetic signal and the relationship between phylogenetic relatedness and ecological similarity among species. Ecol. Lett. 11(10), 995–1003 (2008).
Hutter, C. R., Guayasamin, J. M. & Wiens, J. J. Explaining Andean megadiversity: the evolutionary and ecological causes of glassfrog elevational richness patterns. Ecol. Lett. 16(9), 1135–1144 (2013).
Pough, H. & Magnusson, W. E. Behavioral energetics. In Environmental Physiology of the Amphibians (eds Feder, M. E. & Warren, W. B.) (University of Chicago Press, Chicago, 1992).
Phillips, B. L., Brown, G. P., Webb, J. K. & Shine, R. Invasion and the evolution of speed in toads. Nature 439(7078), 803 (2006).
Hof, C., Araújo, M. B., Jetz, W. & Rahbek, C. Additive threats from pathogens, climate and land-use change for global amphibian diversity. Nature 480(7378), 516 (2011).
Cadotte, M. W. & Jonathan, D. T. Rarest of the rare: advances in combining evolutionary distinctiveness and scarcity to inform conservation at biogeographical scales. Divers. Distrib. 16(3), 376–385 (2010).
Casacci, L. P., Barbero, F. & Balletto, E. The, “Evolutionarily Significant Unit” concept and its applicability in biological conservation. Ital. J. Zool. 81(2), 182–193 (2014).
Enriquez‐Urzelai, U., Kearney, M. R., Nicieza, A. G., & Tingley, R. Integrating mechanistic and correlative niche models to unravel range‐limiting processes in a temperate amphibian. Glob. Change Biol. (2019).
Caeiro-Dias, G. et al. Lack of congruence of genetic and niche divergence in Podarcis hispanicus complex. J. Zool. Syst. Evol. Res. 56(4), 479–492 (2018).
Raes, N. & ter Steege, H. A null-model for significance testing of presence-only species distribution models. Ecography 30(5), 727–736 (2007).
Research funds provided by the following projects of Spanish Ministry of Science and Innovation: CGL 2008–04814-C02/BOS (JFB), CGL2011-25062 (RM), CGL2017-86924-P (MT and AGN), CGL2017-88764-R (DLL) and and CGL2014-56416-P (PA). DLL also acknowledges a post-doctoral study grant by the Comunidad de Madrid (Atracción de Talento Investigador, 2016-T2/AMB-1722, CAM, Spain).
The authors declare no competing interests.
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Rodríguez-Rodríguez, E.J., Beltrán, J.F., Tejedo, M. et al. Niche models at inter- and intraspecific levels reveal hierarchical niche differentiation in midwife toads. Sci Rep 10, 10942 (2020). https://doi.org/10.1038/s41598-020-67992-6