Environmental niche modelling fails to predict Last Glacial Maximum refugia: niche shifts, microrefugia or incorrect palaeoclimate estimates?

AIM: Many predictions of responses to future climate change utilize ecological niche models (ENMs). We assess the capacity of these models to predict species distributions under conditions that differ from the current environment by testing whether they can predict past distributions of species. LOC...

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Published inGlobal ecology and biogeography Vol. 23; no. 11; pp. 1186 - 1197
Main Authors Worth, James R. P, Williamson, Grant J, Sakaguchi, Shota, Nevill, Paul G, Jordan, Greg J
Format Journal Article
LanguageEnglish
Published Oxford Blackwell Science 01.11.2014
Blackwell Publishing Ltd
John Wiley & Sons Ltd
Blackwell
Wiley Subscription Services, Inc
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Summary:AIM: Many predictions of responses to future climate change utilize ecological niche models (ENMs). We assess the capacity of these models to predict species distributions under conditions that differ from the current environment by testing whether they can predict past distributions of species. LOCATION: From 43° S to 31° S in south‐eastern Australia (including Tasmania). METHODS: We studied three dominant tree species of temperate Australian mesic forests, Atherosperma moschatum, Eucalyptus regnans and Nothofagus cunninghamii. Phylogeographic evidence indicates that these species each survived the Last Glacial Maximum (LGM) in multiple refugia. We modelled the current distribution of each species and projected those models onto LGM climates under six palaeoclimatic scenarios. The support for phylogeographic‐based glacial refugia was estimated under each scenario using three different thresholds for inferring species presence/absence. RESULTS: The LGM models under scenarios that allowed for a realistic level of rainfall failed to predict survival of the study species in refugia identified from genetic evidence, apart from those in perhumid western Tasmania. MAIN CONCLUSIONS: Correct prediction of nearly all modern occurrences of the species suggests that this failure of ENMs to predict refugial survival was not methodological. Rather we conclude that the existing realized niches of these species may have changed since the LGM. Such niche changes may have involved the occurrence of non‐analogue climates in the LGM and some significant alteration of fundamental niche (for at least E. regnans). Our results emphasize that predictions of future impacts of climate change on biodiversity will benefit from awareness of the limitations of ENMs in predicting the extinction of populations/species. Greater knowledge of how niches have changed through time and how this relates to the characteristics of species is needed to improve the reliability of ENMs. Niche changes in plants may also affect palaeoclimatic estimates based on fossil pollen.
Bibliography:http://dx.doi.org/10.1111/geb.12239
ArticleID:GEB12239
Australian Research Council - No. DP120100501
ark:/67375/WNG-6CS1G6DQ-S
istex:C927EDC99952CC5894B5B3956A88D8014691833C
Appendix S1 Table of Last Glacial Maximum climates derived from palaeoproxy evidence versus those derived from four general circulation models. Appendix S2 Genetic based refugial areas for Atherosperma moschatum. Appendix S3 Genetic based refugial areas for Eucalyptus regnans. Appendix S4 Genetic based refugial areas for Nothofagus cunninghamii. Appendix S5 Modelled current distribution of Atherosperma moschatum. Appendix S6 Modelled Last Glacial Maximum range of Atherosperma moschatum under two general circulation models and three levels of rainfall. Appendix S7 Areas affected by clamping for Atherosperma moschatum. Appendix S8 The percentage support for each Atherosperma moschatum genetic based refugial area under each of the six Last Glacial Maximum climate models. Appendix S9 Modelled current distribution of Eucalyptus regnans. Appendix S10 Modelled Last Glacial Maximum range of Eucalyptus regnans under two general circulation models and three levels of rainfall. Appendix S11 Areas affected by clamping for Eucalyptus regnans. Appendix S12 The percentage support for each Eucalyptus regnans genetic based refugial area under each of the six Last Glacial Maximum climate models. Appendix S13 Modelled current distribution of Nothofagus cunninghamii. Appendix S14 Modelled Last Glacial Maximum range of Nothofagus cunninghamii under two general circulation models and three levels of rainfall. Appendix S15 Areas affected by clamping for Nothofagus cunninghamii. Appendix S16 The percentage support for each Nothofagus cunninghamii genetic based refugial area under each of the six Last Glacial Maximum climate models.
Japanese Society for the Promotion of Science Postdoctoral Research Fellowship
ObjectType-Article-1
SourceType-Scholarly Journals-1
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ISSN:1466-822X
1466-8238
DOI:10.1111/geb.12239