2016
DOI: 10.1002/ecy.1489
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Does habitat unpredictability promote the evolution of a colonizer syndrome in amphibian metapopulations?

Abstract: Dispersal is a central component of life history evolution. An increasing number of studies suggest that spatiotemporally variable environments may promote the evolution of "dispersal syndromes," consisting of covariation patterns between dispersal and morphological, physiological, behavioral, and life history traits. At the interspecific scale, the "colonizer syndrome" appears to be one of the most frequently recorded associations between dispersal and life history traits, linking a high dispersal rate, high … Show more

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Cited by 40 publications
(79 citation statements)
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References 79 publications
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“…This result confirms the conclusion of a previous study (Cayuela et al 2016a), which found high dispersal rates in metapopulations of yellow-bellied toads occurring in forest environments. The estimate precision also suggests that temporal effects or covariate effects could be detected if present in the parameter space we explored.…”
Section: Discussionsupporting
confidence: 93%
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“…This result confirms the conclusion of a previous study (Cayuela et al 2016a), which found high dispersal rates in metapopulations of yellow-bellied toads occurring in forest environments. The estimate precision also suggests that temporal effects or covariate effects could be detected if present in the parameter space we explored.…”
Section: Discussionsupporting
confidence: 93%
“…), which leads to frequent breeding failure (Barandun et al 1997). Dispersal events occur between these groups of ponds (Cayuela et al 2016a) at both intra-annual and interannual scales; we made a distinction between these two types of dispersal event as they likely rely on different causal factors in amphibians (Deno€ el et al 2018). This metapopulation occupies 84 pond networks spread over a woodland and covering a surface area of 9,600 ha.…”
Section: Model 1: Yellow-bellied Toad Datamentioning
confidence: 99%
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“…It is protected by national legislation over much of its range and is registered in Appendix II of the Bern Convention and Appendices II and IV of the EU Habitat Directive. In harvested forests, B. variegata breeds in artificial waterbodies (e.g., ruts and residual puddles) resulting from logging operations (Barandun, Reyer, & Anholt, ; Cayuela, Boualit, et al., 2016). We analysed the effects of patch destruction on adult survival and the long‐term population growth rate in an SSP consisting of 28 breeding patches (i.e., discrete groups of waterbodies).…”
Section: Introductionmentioning
confidence: 99%
“…For that purpose, we used recently developed capture–recapture (CR) multievent models (Cayuela, Pradel, Joly, Bonnaire, & Besnard, ) to estimate survival depending on patch status (i.e., still available or destroyed through environmental rehabilitation) and dispersal, including whether individuals dispersed freely (i.e., facultative dispersal from available patches) or in response to patch loss (i.e., forced dispersal from a destroyed patch). We formulated the following hypotheses about intra‐annual and interannual dispersal: (a) Facultative dispersal was expected to be high in SSPs of B. variegata occurring in forest environments due to spatiotemporal variation in patch characteristics (Cayuela, Boualit, et al., 2016). (b) Dispersal was also expected to be female biased as males of this species display territorial behaviour (Schneider & Eichelberg, ) and females spread their eggs between distinct breeding patches (Buschmann, ).…”
Section: Introductionmentioning
confidence: 99%