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The joint effects of forest habitat area and fragmentation on dung beetles

Habitat loss and habitat fragmentation usually occur together, at the same time and place. However, while there is a consensus that habitat loss is the preeminent threat to biodiversity, the effects of fragmentation are contentious. Some argue that habitat fragmentation is not bad for biodiversity,...

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Autores principales: Mbora, David Nyaga Mugo, Mutua, Morris Nzioka
Formato: Online Artículo Texto
Lenguaje:English
Publicado: John Wiley and Sons Inc. 2023
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10451379/
https://www.ncbi.nlm.nih.gov/pubmed/37636869
http://dx.doi.org/10.1002/ece3.10429
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author Mbora, David Nyaga Mugo
Mutua, Morris Nzioka
author_facet Mbora, David Nyaga Mugo
Mutua, Morris Nzioka
author_sort Mbora, David Nyaga Mugo
collection PubMed
description Habitat loss and habitat fragmentation usually occur together, at the same time and place. However, while there is a consensus that habitat loss is the preeminent threat to biodiversity, the effects of fragmentation are contentious. Some argue that habitat fragmentation is not bad for biodiversity, and even that it is good. Generally, the studies that find no harm or positive outcomes of fragmentation invariably assume that it is independent of habitat loss. However, dissociating the effects of habitat fragmentation from habitat loss is questionable because the two are essentially coupled. Accordingly, we evaluated how forest area and fragmentation (via edge effects) influenced dung beetles per se, and through their effects on the abundance of mammals, using structural equation modeling (SEM). Dung beetles are very sensitive to forest habitat loss and fragmentation and to changes in the abundance of mammals on which they depend for dung. Our study area was in the Tana River, Kenya, where forest fragments are depauperated of mammals except for two endemic species of monkeys. We mapped 12 forests, counted the resident monkeys, and sampled 113,955 beetles from 288 plots. Most of the 87 species of beetles found were small tunnellers. After implementing a fully latent Structural Regression SEM, the optimal model explained a significant 26% of the variance in abundance, and 89% of diversity. The main drivers of beetle abundance were positive, direct, effects of forest area and number of monkeys, and negative edge effects. The main drivers of diversity were the direct effects of the beetle abundance, indirect effects of forest area and abundance of mammals, and indirect negative edge effects. Thus, forest area, fragmentation (via edge effects), and the number of monkeys jointly influenced the abundance and diversity of the beetles directly and indirectly.
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spelling pubmed-104513792023-08-26 The joint effects of forest habitat area and fragmentation on dung beetles Mbora, David Nyaga Mugo Mutua, Morris Nzioka Ecol Evol Research Articles Habitat loss and habitat fragmentation usually occur together, at the same time and place. However, while there is a consensus that habitat loss is the preeminent threat to biodiversity, the effects of fragmentation are contentious. Some argue that habitat fragmentation is not bad for biodiversity, and even that it is good. Generally, the studies that find no harm or positive outcomes of fragmentation invariably assume that it is independent of habitat loss. However, dissociating the effects of habitat fragmentation from habitat loss is questionable because the two are essentially coupled. Accordingly, we evaluated how forest area and fragmentation (via edge effects) influenced dung beetles per se, and through their effects on the abundance of mammals, using structural equation modeling (SEM). Dung beetles are very sensitive to forest habitat loss and fragmentation and to changes in the abundance of mammals on which they depend for dung. Our study area was in the Tana River, Kenya, where forest fragments are depauperated of mammals except for two endemic species of monkeys. We mapped 12 forests, counted the resident monkeys, and sampled 113,955 beetles from 288 plots. Most of the 87 species of beetles found were small tunnellers. After implementing a fully latent Structural Regression SEM, the optimal model explained a significant 26% of the variance in abundance, and 89% of diversity. The main drivers of beetle abundance were positive, direct, effects of forest area and number of monkeys, and negative edge effects. The main drivers of diversity were the direct effects of the beetle abundance, indirect effects of forest area and abundance of mammals, and indirect negative edge effects. Thus, forest area, fragmentation (via edge effects), and the number of monkeys jointly influenced the abundance and diversity of the beetles directly and indirectly. John Wiley and Sons Inc. 2023-08-25 /pmc/articles/PMC10451379/ /pubmed/37636869 http://dx.doi.org/10.1002/ece3.10429 Text en © 2023 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd. https://creativecommons.org/licenses/by/4.0/This is an open access article under the terms of the http://creativecommons.org/licenses/by/4.0/ (https://creativecommons.org/licenses/by/4.0/) License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
spellingShingle Research Articles
Mbora, David Nyaga Mugo
Mutua, Morris Nzioka
The joint effects of forest habitat area and fragmentation on dung beetles
title The joint effects of forest habitat area and fragmentation on dung beetles
title_full The joint effects of forest habitat area and fragmentation on dung beetles
title_fullStr The joint effects of forest habitat area and fragmentation on dung beetles
title_full_unstemmed The joint effects of forest habitat area and fragmentation on dung beetles
title_short The joint effects of forest habitat area and fragmentation on dung beetles
title_sort joint effects of forest habitat area and fragmentation on dung beetles
topic Research Articles
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10451379/
https://www.ncbi.nlm.nih.gov/pubmed/37636869
http://dx.doi.org/10.1002/ece3.10429
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