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Amphibian and reptile communities and functional groups over a land‐use gradient in a coastal tropical forest landscape of high richness and endemicity

Amphibian and reptile communities and functional groups over a land‐use gradient in a coastal... Information on the response of herpetofauna to different land uses is limited although important for land‐use planning to support conservation in human‐modified landscapes. Although transformation is dogmatically associated with extinction, species respond idiosyncratically to land‐use change, and persistence of species in habitat fragments may depend on careful management of the human‐modified matrix. We sampled herpetofauna over a vegetation‐type gradient representative of regional land uses [old‐growth forest, degraded forest, acacia woodland (i.e. new‐growth forest), eucalyptus plantation and sugar cane cultivation] in the forest belt skirting the southeastern coast of Africa, part of a biodiversity hotspot hosting many endemic herpetofaunal species in a highly transformed landscape. We categorized species into trait‐derived functional groups, and assessed abundance and richness of groups and compared community metrics along the gradient. We further assessed the capacity of environmental variables to predict richness and abundance. Overall, old‐growth forest harbored the highest richness and abundance, and amphibians and reptiles responded similarly to the gradient. Richness was low in cultivation, and surprisingly, in degraded forest, but substantial in acacia woodland and plantation. Composition differed between natural vegetation types (forest, degraded forest) and anthropogenic types (plantation, cultivation), while acacia woodland grouped with the latter for amphibians and the former for reptiles. Functional group richness eroded along the gradient, a pattern driven by the sensitivity of fossorial/ground‐dependent amphibians (A2) and reptiles (R2) and vegetation‐dwelling amphibians (A4) to habitat change. Variables describing temperature, cover and soil were good predictors of amphibian abundance, particularly of functional groups, but not for reptiles. Conserving forest and preventing degradation is important for forest herpetofaunal conservation, restoration and plantations have intermediate value, and cultivation is least beneficial. Our study demonstrates the utility of function‐related assessments, beyond traditional metrics alone, for understanding community responses to transformation. Particularly, fossorial/ground‐dependent amphibians and reptiles, and vegetation‐dwelling amphibians should be closely monitored. http://www.deepdyve.com/assets/images/DeepDyve-Logo-lg.png Animal Conservation Wiley

Amphibian and reptile communities and functional groups over a land‐use gradient in a coastal tropical forest landscape of high richness and endemicity

Trimble, M. J.; Aarde, R. J.
Animal Conservation , Volume 17 (5) – Jan 1, 2014
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References (86)

Publisher
Wiley
Copyright
Animal Conservation © 2014 The Zoological Society of London
ISSN
1367-9430
eISSN
1469-1795
DOI
10.1111/acv.12111
Publisher site
See Article on Publisher Site

Abstract

Information on the response of herpetofauna to different land uses is limited although important for land‐use planning to support conservation in human‐modified landscapes. Although transformation is dogmatically associated with extinction, species respond idiosyncratically to land‐use change, and persistence of species in habitat fragments may depend on careful management of the human‐modified matrix. We sampled herpetofauna over a vegetation‐type gradient representative of regional land uses [old‐growth forest, degraded forest, acacia woodland (i.e. new‐growth forest), eucalyptus plantation and sugar cane cultivation] in the forest belt skirting the southeastern coast of Africa, part of a biodiversity hotspot hosting many endemic herpetofaunal species in a highly transformed landscape. We categorized species into trait‐derived functional groups, and assessed abundance and richness of groups and compared community metrics along the gradient. We further assessed the capacity of environmental variables to predict richness and abundance. Overall, old‐growth forest harbored the highest richness and abundance, and amphibians and reptiles responded similarly to the gradient. Richness was low in cultivation, and surprisingly, in degraded forest, but substantial in acacia woodland and plantation. Composition differed between natural vegetation types (forest, degraded forest) and anthropogenic types (plantation, cultivation), while acacia woodland grouped with the latter for amphibians and the former for reptiles. Functional group richness eroded along the gradient, a pattern driven by the sensitivity of fossorial/ground‐dependent amphibians (A2) and reptiles (R2) and vegetation‐dwelling amphibians (A4) to habitat change. Variables describing temperature, cover and soil were good predictors of amphibian abundance, particularly of functional groups, but not for reptiles. Conserving forest and preventing degradation is important for forest herpetofaunal conservation, restoration and plantations have intermediate value, and cultivation is least beneficial. Our study demonstrates the utility of function‐related assessments, beyond traditional metrics alone, for understanding community responses to transformation. Particularly, fossorial/ground‐dependent amphibians and reptiles, and vegetation‐dwelling amphibians should be closely monitored.

Journal

Animal Conservation – Wiley

Published: Jan 1, 2014

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