4.3 Article

Fine scale genetic structure in fire salamanders (Salamandra salamandra) along a rural-to-urban gradient

期刊

CONSERVATION GENETICS
卷 22, 期 2, 页码 275-292

出版社

SPRINGER
DOI: 10.1007/s10592-021-01335-4

关键词

Amphibians; Bayesian clustering; Gene diversity; Landscape genetics; Isolation-by-distance; Isolation-by-barrier

资金

  1. Office Federal de l'Environnement
  2. Centre de Conservation de la Faune du Canton de Vaud
  3. MAVA Foundation
  4. Agassiz Foundation
  5. Societe Academique Vaudoise

向作者/读者索取更多资源

Delineating population boundaries in anthropogenic landscapes is crucial for biology domains focusing on ecology, evolution, and conservation. This task is particularly challenging for amphibian species reproducing in aquatic habitats but living in terrestrial habitats, highlighting the difficulty of defining management units in open systems.
Delineating population boundaries in anthropogenic landscape is of critical importance for domains of biology that are concerned with the ecology, evolution and conservation of species. This remains particularly difficult for species where there is no obvious demarcation of geographical populations and dispersal patterns are poorly known. This is often the case in amphibian species that reproduce in aquatic habitats but live otherwise in terrestrial habitats. Sampling of such species usually occurs in the aquatic habitat (i.e., breeding sites) but these may represent neither genetically nor demographically distinct populations. Here, we analyzed the genetic structure of a stream-breeding species, the fire salamander (Salamandra salamandra) along a rural-to-urban land use gradient. We used genetic data and Bayesian clustering approaches, which rely on genetic information without assuming predefined populations, to delineate distinctive genetic units along this gradient, and compare genetic diversity between rural and urban areas. The different analytical approaches used partitioned our dataset in slightly different but highly congruent clusters, that included localities which were up to 19 km apart from each other. Genetic breaks occurred at unexpected places while several landscape features reported to act as barriers on gene flow for amphibians did not lead to genetic breaks. Our results emphasize the difficulty to delineate management units in open systems, especially for long-lived species, for which the timespan between the establishment of a barrier and its translation into clear genetic breaks will take longer than in short-lived species.

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