Which randomizations detect convergence and divergence in trait-based community assembly? A test of commonly used null models

Questions: Mechanisms of community assembly are increasingly explored by combining community and species trait data with null models. By investigating if the traits of existing species are more similar (trait convergence) or more dissimilar (trait divergence) than expected by chance, these tests rel...

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Published inJournal of vegetation science Vol. 27; no. 6; pp. 1275 - 1287
Main Authors Götzenberger, Lars, Botta-Dukát, Zoltán, Lepš, Jan, Pärtel, Meelis, Zobel, Martin, de Bello, Francesco
Format Journal Article
LanguageEnglish
Published Blackwell Publishing Ltd 01.11.2016
John Wiley & Sons Ltd
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ISSN1100-9233
1654-1103
DOI10.1111/jvs.12452

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Summary:Questions: Mechanisms of community assembly are increasingly explored by combining community and species trait data with null models. By investigating if the traits of existing species are more similar (trait convergence) or more dissimilar (trait divergence) than expected by chance, these tests relate observed patterns to different existence mechanisms. Do null models accurately detect trait convergence and divergence? Are different null models equally good at detecting these two opposing patterns? How important are the species pool and other constraints that are considered by different null models? Methods: We applied ten common randomizations to communities that were simulated in a process-based model. Results: Null models good at detecting biotic processes differed from those null models that revealed abiotic processes. In particular, limiting similarity (detected through divergence) was better detected by randomizations that release the link between species abundance and trait values, whereas environmental filtering (detected through convergence of an environmental response trait) was identified by randomizations that keep this link. In general, using species abundance data provided better results than using presence-absence data, particularly within given limited environmental conditions. Weaker competitor exclusion (detected through convergence of a competition-related trait) was only detected when no environmental filtering was acting on the simulated assembly, which points to difficulties in disentangling biotic and abiotic convergence in natural communities, especially when data are randomized across habitats. Conclusions: Overall the results manifest the importance of the pool of species over which randomizations are applied; in particular whether randomizations are conducted across or within given habitats. Taken together, our findings show that different null models must be combined and applied to a carefully chosen pool of species and species abundance data to ensure that co-existence mechanisms can be properly assessed. We utilize the results to (1) discuss how different constraints implied in the different null models affect the outcomes of our tests, and (2) provide some basic recommendations on how to choose null models, given the data available and questions being asked.
Bibliography:ark:/67375/WNG-4L7943ZX-G
Appendix S1. Detailed description of the community simulation model used in the study.Appendix S2. Scheme of the data used for null model-based studies of community assembly.Appendix S3. Detailed description of the tested null models.Appendix S4. Tables of results of the Type I error and power analyses.Appendix S5. Rank-abundance curves for three selected simulated communities
European Union through the European Regional Development Fund, Centre of Excellence EcolChange
Czech Science Foundation (GACR) - No. P505/12/1296
European Union Seventh Framework Programme for research, technological development and demonstration - No. GA-2010-267243
Estonian Ministry of Education and Research, institutional research funding
istex:100E710053F5D6D780A46E95B0A9C27C6BC75110
Hungarian Science Fund - No. K83595
ArticleID:JVS12452
ObjectType-Article-1
SourceType-Scholarly Journals-1
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ISSN:1100-9233
1654-1103
DOI:10.1111/jvs.12452