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Coral cover a stronger driver of reef fish trophic biomass than fishing

An influential paradigm in coral reef ecology is that fishing causes trophic cascades through reef fish assemblages, resulting in reduced herbivory and thus benthic phase shifts from coral to algal dominance. Few long‐term field tests exist of how fishing affects the trophic structure of coral reef...

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Autores principales: Russ, Garry R., Rizzari, Justin R., Abesamis, Rene A., Alcala, Angel C.
Formato: Online Artículo Texto
Lenguaje:English
Publicado: John Wiley and Sons Inc. 2020
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7816266/
https://www.ncbi.nlm.nih.gov/pubmed/32866333
http://dx.doi.org/10.1002/eap.2224
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author Russ, Garry R.
Rizzari, Justin R.
Abesamis, Rene A.
Alcala, Angel C.
author_facet Russ, Garry R.
Rizzari, Justin R.
Abesamis, Rene A.
Alcala, Angel C.
author_sort Russ, Garry R.
collection PubMed
description An influential paradigm in coral reef ecology is that fishing causes trophic cascades through reef fish assemblages, resulting in reduced herbivory and thus benthic phase shifts from coral to algal dominance. Few long‐term field tests exist of how fishing affects the trophic structure of coral reef fish assemblages, and how such changes affect the benthos. Alternatively, benthic change itself may drive the trophic structure of reef fish assemblages. Reef fish trophic structure and benthic cover were quantified almost annually from 1983 to 2014 at two small Philippine islands (Apo, Sumilon). At each island a No‐Take Marine Reserve (NTMR) site and a site open to subsistence reef fishing were monitored. Thirteen trophic groups were identified. Large planktivores often accounted for >50% of assemblage biomass. Significant NTMR effects were detected at each island for total fish biomass, but for only 2 of 13 trophic components: generalist large predators and large planktivores. Fishing‐induced changes in biomass of these components had no effect on live hard coral (HC) cover. In contrast, HC cover affected biomass of 11 of 13 trophic components significantly. Positive associations with HC cover were detected for total fish biomass, generalist large predators, piscivores, obligate coral feeders, large planktivores, and small planktivores. Negative associations with HC cover were detected for large benthic foragers, detritivores, excavators, scrapers, and sand feeders. These associations of fish biomass to HC cover were most clear when environmental disturbances (e.g., coral bleaching, typhoons) reduced HC cover, often quickly (1–2 yr), and when HC recovered, often slowly (5–10 yr). As HC cover changed, the biomass of 11 trophic components of the fish assemblage changed. Benthic and fish assemblages were distinct at all sites from the outset, remaining so for 31 yr, despite differences in fishing pressure and disturbance history. HC cover alone explained ~30% of the variability in reef fish trophic structure, whereas fishing alone explained 24%. Furthermore, HC cover affected more trophic groups more strongly than fishing. Management of coral reefs must include measures to maintain coral reef habitats, not just measures to reduce fishing by NTMRs.
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spelling pubmed-78162662021-01-27 Coral cover a stronger driver of reef fish trophic biomass than fishing Russ, Garry R. Rizzari, Justin R. Abesamis, Rene A. Alcala, Angel C. Ecol Appl Articles An influential paradigm in coral reef ecology is that fishing causes trophic cascades through reef fish assemblages, resulting in reduced herbivory and thus benthic phase shifts from coral to algal dominance. Few long‐term field tests exist of how fishing affects the trophic structure of coral reef fish assemblages, and how such changes affect the benthos. Alternatively, benthic change itself may drive the trophic structure of reef fish assemblages. Reef fish trophic structure and benthic cover were quantified almost annually from 1983 to 2014 at two small Philippine islands (Apo, Sumilon). At each island a No‐Take Marine Reserve (NTMR) site and a site open to subsistence reef fishing were monitored. Thirteen trophic groups were identified. Large planktivores often accounted for >50% of assemblage biomass. Significant NTMR effects were detected at each island for total fish biomass, but for only 2 of 13 trophic components: generalist large predators and large planktivores. Fishing‐induced changes in biomass of these components had no effect on live hard coral (HC) cover. In contrast, HC cover affected biomass of 11 of 13 trophic components significantly. Positive associations with HC cover were detected for total fish biomass, generalist large predators, piscivores, obligate coral feeders, large planktivores, and small planktivores. Negative associations with HC cover were detected for large benthic foragers, detritivores, excavators, scrapers, and sand feeders. These associations of fish biomass to HC cover were most clear when environmental disturbances (e.g., coral bleaching, typhoons) reduced HC cover, often quickly (1–2 yr), and when HC recovered, often slowly (5–10 yr). As HC cover changed, the biomass of 11 trophic components of the fish assemblage changed. Benthic and fish assemblages were distinct at all sites from the outset, remaining so for 31 yr, despite differences in fishing pressure and disturbance history. HC cover alone explained ~30% of the variability in reef fish trophic structure, whereas fishing alone explained 24%. Furthermore, HC cover affected more trophic groups more strongly than fishing. Management of coral reefs must include measures to maintain coral reef habitats, not just measures to reduce fishing by NTMRs. John Wiley and Sons Inc. 2020-10-03 2021-01 /pmc/articles/PMC7816266/ /pubmed/32866333 http://dx.doi.org/10.1002/eap.2224 Text en © 2020 The Authors. Ecological Applications published by Wiley Periodicals LLC on behalf of Ecological Society of America This is an open access article under the terms of the http://creativecommons.org/licenses/by-nc-nd/4.0/ License, which permits use and distribution in any medium, provided the original work is properly cited, the use is non‐commercial and no modifications or adaptations are made.
spellingShingle Articles
Russ, Garry R.
Rizzari, Justin R.
Abesamis, Rene A.
Alcala, Angel C.
Coral cover a stronger driver of reef fish trophic biomass than fishing
title Coral cover a stronger driver of reef fish trophic biomass than fishing
title_full Coral cover a stronger driver of reef fish trophic biomass than fishing
title_fullStr Coral cover a stronger driver of reef fish trophic biomass than fishing
title_full_unstemmed Coral cover a stronger driver of reef fish trophic biomass than fishing
title_short Coral cover a stronger driver of reef fish trophic biomass than fishing
title_sort coral cover a stronger driver of reef fish trophic biomass than fishing
topic Articles
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7816266/
https://www.ncbi.nlm.nih.gov/pubmed/32866333
http://dx.doi.org/10.1002/eap.2224
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