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Validating graph-based connectivity models with independent presence–absence and genetic data sets
Authors:Alexandrine Daniel  Paul Savary  Jean-Christophe Foltête  Aurélie Khimoun  Bruno Faivre  Anthony Ollivier  Cyril Éraud  Hervé Moal  Gilles Vuidel  Stéphane Garnier
Institution:1. Biogéosciences, UMR 6282 CNRS, Université Bourgogne-Franche-Comté, Dijon, France;2. Biogéosciences, UMR 6282 CNRS, Université Bourgogne-Franche-Comté, Dijon, France

ThéMA, UMR 6049 CNRS, Université de Franche-Comté, Besançon, France

ARP-Astrance, Paris, France;3. ThéMA, UMR 6049 CNRS, Université de Franche-Comté, Besançon, France;4. Office Français de la Biodiversité, Chizé, France;5. ARP-Astrance, Paris, France

Abstract:Habitat connectivity is a key objective of current conservation policies and is commonly modeled by landscape graphs (i.e., sets of habitat patches nodes] connected by potential dispersal paths links]). These graphs are often built based on expert opinion or species distribution models (SDMs) and therefore lack empirical validation from data more closely reflecting functional connectivity. Accordingly, we tested whether landscape graphs reflect how habitat connectivity influences gene flow, which is one of the main ecoevolutionary processes. To that purpose, we modeled the habitat network of a forest bird (plumbeous warbler Setophaga plumbea]) on Guadeloupe with graphs based on expert opinion, Jacobs’ specialization indices, and an SDM. We used genetic data (712 birds from 27 populations) to compute local genetic indices and pairwise genetic distances. Finally, we assessed the relationships between genetic distances or indices and cost distances or connectivity metrics with maximum-likelihood population-effects distance models and Spearman correlations between metrics. Overall, the landscape graphs reliably reflected the influence of connectivity on population genetic structure; validation R2 was up to 0.30 and correlation coefficients were up to 0.71. Yet, the relationship among graph ecological relevance, data requirements, and construction and analysis methods was not straightforward because the graph based on the most complex construction method (species distribution modeling) sometimes had less ecological relevance than the others. Cross-validation methods and sensitivity analyzes allowed us to make the advantages and limitations of each construction method spatially explicit. We confirmed the relevance of landscape graphs for conservation modeling but recommend a case-specific consideration of the cost-effectiveness of their construction methods. We hope the replication of independent validation approaches across species and landscapes will strengthen the ecological relevance of connectivity models.
Keywords:conservation modeling  habitat connectivity  landscape genetics  landscape graphs  species distribution models  conectividad de hábitats  grafos de paisaje  genética de paisajes  modelos para la conservación  modelos de distribución de especies
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