Decadal‐scale response of detritivorous surgeonfishes (family Acanthuridae) to no‐take marine reserve protection and changes in benthic habitat
No‐take marine reserves (NTMR) are increasingly being implemented to mitigate the effects of fishing on coral reefs, yet determining the efficacy of NTMRs depends largely on partitioning the effects of fishing from the effect of benthic habitat. Species of coral‐reef fishes typically decline in dens...
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Veröffentlicht in: | Journal of fish biology 2018-11, Vol.93 (5), p.887-900 |
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creator | Russ, Garry R. Payne, Cody S. Bergseth, Brock J. Rizzari, Justin R. Abesamis, Rene A. Alcala, Angel C. |
description | No‐take marine reserves (NTMR) are increasingly being implemented to mitigate the effects of fishing on coral reefs, yet determining the efficacy of NTMRs depends largely on partitioning the effects of fishing from the effect of benthic habitat. Species of coral‐reef fishes typically decline in density when subjected to fishing or benthic disturbances, but this is not always the case. This study documents the long‐term (8–31 years) response of six species of detritivorous surgeonfishes (family Acanthuridae) to NTMR protection and benthic habitat change at four islands (Apo, Sumilon, Mantigue, Selinog) in the central Philippines, each island with a NTMR and a monitored fished site. Despite being subject to moderate fishing pressure, these species did not increase in density with NTMR protection. However, density of these surgeonfishes had a strong negative relationship with cover of live hard coral and a strong positive relationship with cover of dead substratum (sand, rubble, hard dead substratum). These surgeonfishes typically feed over dead substrata and thus probably increase in density following large environmental disturbances that substantially reduce live hard coral cover. Here, we describe effects of environmental disturbance events (e.g., use of explosives, typhoons) that reduced live hard‐coral cover and subsequent large increases (up to 25 fold) in surgeonfish densities, which then slowly (over 5–15 years) decreased in density as live hard coral recovered. Density of these functionally important surgeonfish species was influenced more by changes to benthic cover than by NTMR protection. Thus, we highlight the greater importance of bottom‐up controls (i.e., benthic changes to food availability) than top‐down control (i.e., fishing) on a functionally important group of coral‐reef fishes. |
doi_str_mv | 10.1111/jfb.13809 |
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Species of coral‐reef fishes typically decline in density when subjected to fishing or benthic disturbances, but this is not always the case. This study documents the long‐term (8–31 years) response of six species of detritivorous surgeonfishes (family Acanthuridae) to NTMR protection and benthic habitat change at four islands (Apo, Sumilon, Mantigue, Selinog) in the central Philippines, each island with a NTMR and a monitored fished site. Despite being subject to moderate fishing pressure, these species did not increase in density with NTMR protection. However, density of these surgeonfishes had a strong negative relationship with cover of live hard coral and a strong positive relationship with cover of dead substratum (sand, rubble, hard dead substratum). These surgeonfishes typically feed over dead substrata and thus probably increase in density following large environmental disturbances that substantially reduce live hard coral cover. Here, we describe effects of environmental disturbance events (e.g., use of explosives, typhoons) that reduced live hard‐coral cover and subsequent large increases (up to 25 fold) in surgeonfish densities, which then slowly (over 5–15 years) decreased in density as live hard coral recovered. Density of these functionally important surgeonfish species was influenced more by changes to benthic cover than by NTMR protection. Thus, we highlight the greater importance of bottom‐up controls (i.e., benthic changes to food availability) than top‐down control (i.e., fishing) on a functionally important group of coral‐reef fishes.</description><identifier>ISSN: 0022-1112</identifier><identifier>EISSN: 1095-8649</identifier><identifier>DOI: 10.1111/jfb.13809</identifier><identifier>PMID: 30246331</identifier><language>eng</language><publisher>Oxford, UK: Blackwell Publishing Ltd</publisher><subject>Acanthuridae ; Animals ; Anthozoa - physiology ; Aquatic habitats ; benthic habitat ; Catch per unit effort ; Conservation of Natural Resources - methods ; Coral Reefs ; Corals ; coral‐reef fish ; Cyclonic Storms ; Density ; detritivores ; Disturbances ; Ecosystem ; environmental disturbance ; Environmental effects ; Explosives ; Fishes - physiology ; Fishing ; Fishing effort ; Fishing pressure ; Food availability ; Food supply ; Habitat changes ; Habitats ; Hurricanes ; Marine invertebrates ; Marine parks ; no‐take reserves ; Philippines ; Population Dynamics ; Protection ; Species ; Stress, Physiological ; Substrata ; Typhoons</subject><ispartof>Journal of fish biology, 2018-11, Vol.93 (5), p.887-900</ispartof><rights>2018 The Fisheries Society of the British Isles</rights><rights>2018 The Fisheries Society of the British Isles.</rights><rights>Journal of Fish Biology © 2018 The Fisheries Society of the British Isles</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3889-89d2de902a20ccce661acabffc3cfec411cc81db644302b216f7df7817ee1a533</citedby><cites>FETCH-LOGICAL-c3889-89d2de902a20ccce661acabffc3cfec411cc81db644302b216f7df7817ee1a533</cites><orcidid>0000-0002-5486-175X</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1111%2Fjfb.13809$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1111%2Fjfb.13809$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,780,784,1416,27922,27923,45572,45573</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/30246331$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Russ, Garry R.</creatorcontrib><creatorcontrib>Payne, Cody S.</creatorcontrib><creatorcontrib>Bergseth, Brock J.</creatorcontrib><creatorcontrib>Rizzari, Justin R.</creatorcontrib><creatorcontrib>Abesamis, Rene A.</creatorcontrib><creatorcontrib>Alcala, Angel C.</creatorcontrib><title>Decadal‐scale response of detritivorous surgeonfishes (family Acanthuridae) to no‐take marine reserve protection and changes in benthic habitat</title><title>Journal of fish biology</title><addtitle>J Fish Biol</addtitle><description>No‐take marine reserves (NTMR) are increasingly being implemented to mitigate the effects of fishing on coral reefs, yet determining the efficacy of NTMRs depends largely on partitioning the effects of fishing from the effect of benthic habitat. Species of coral‐reef fishes typically decline in density when subjected to fishing or benthic disturbances, but this is not always the case. This study documents the long‐term (8–31 years) response of six species of detritivorous surgeonfishes (family Acanthuridae) to NTMR protection and benthic habitat change at four islands (Apo, Sumilon, Mantigue, Selinog) in the central Philippines, each island with a NTMR and a monitored fished site. Despite being subject to moderate fishing pressure, these species did not increase in density with NTMR protection. However, density of these surgeonfishes had a strong negative relationship with cover of live hard coral and a strong positive relationship with cover of dead substratum (sand, rubble, hard dead substratum). These surgeonfishes typically feed over dead substrata and thus probably increase in density following large environmental disturbances that substantially reduce live hard coral cover. Here, we describe effects of environmental disturbance events (e.g., use of explosives, typhoons) that reduced live hard‐coral cover and subsequent large increases (up to 25 fold) in surgeonfish densities, which then slowly (over 5–15 years) decreased in density as live hard coral recovered. Density of these functionally important surgeonfish species was influenced more by changes to benthic cover than by NTMR protection. Thus, we highlight the greater importance of bottom‐up controls (i.e., benthic changes to food availability) than top‐down control (i.e., fishing) on a functionally important group of coral‐reef fishes.</description><subject>Acanthuridae</subject><subject>Animals</subject><subject>Anthozoa - physiology</subject><subject>Aquatic habitats</subject><subject>benthic habitat</subject><subject>Catch per unit effort</subject><subject>Conservation of Natural Resources - methods</subject><subject>Coral Reefs</subject><subject>Corals</subject><subject>coral‐reef fish</subject><subject>Cyclonic Storms</subject><subject>Density</subject><subject>detritivores</subject><subject>Disturbances</subject><subject>Ecosystem</subject><subject>environmental disturbance</subject><subject>Environmental effects</subject><subject>Explosives</subject><subject>Fishes - physiology</subject><subject>Fishing</subject><subject>Fishing effort</subject><subject>Fishing pressure</subject><subject>Food availability</subject><subject>Food supply</subject><subject>Habitat changes</subject><subject>Habitats</subject><subject>Hurricanes</subject><subject>Marine invertebrates</subject><subject>Marine parks</subject><subject>no‐take reserves</subject><subject>Philippines</subject><subject>Population Dynamics</subject><subject>Protection</subject><subject>Species</subject><subject>Stress, Physiological</subject><subject>Substrata</subject><subject>Typhoons</subject><issn>0022-1112</issn><issn>1095-8649</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kctuFDEQRS0EIkNgwQ8gS2ySRSd-dDztZQiEhyKxgXWrurqc8dBjD7Y7aHZ8AhJ_yJfgZAILJGpTm6OjW3UZey7FiaxzunbDidSdsA_YQgp71nSmtQ_ZQgilmgqoA_Yk57UQwmqrH7MDLVRrtJYL9vM1IYww_fr-IyNMxBPlbQyZeHR8pJJ88TcxxTnzPKdrisH5vKLMjxxs_LTj5wihrObkR6BjXiIPsboKfCG-geTDnZHSDfFtioWw-Bg4hJHjCsJ1FfnAB6oKj3wFgy9QnrJHDqZMz-73Ift8-ebTxbvm6uPb9xfnVw3qrrNNZ0c1khUKlEBEMkYCwuAcanSErZSInRwH07b13kFJ45ajW3ZySSThTOtDdrT31mRfZ8ql3_iMNE0QqB7cq_q6ZWukERV9-Q-6jnMKNV2ltBXCdPqWOt5TmGLOiVy_Tb5-YddL0d821dem-rumKvvi3jgPGxr_kn-qqcDpHvjmJ9r939R_uHy1V_4GdfCh3g</recordid><startdate>201811</startdate><enddate>201811</enddate><creator>Russ, Garry R.</creator><creator>Payne, Cody S.</creator><creator>Bergseth, Brock J.</creator><creator>Rizzari, Justin R.</creator><creator>Abesamis, Rene A.</creator><creator>Alcala, Angel C.</creator><general>Blackwell Publishing Ltd</general><general>Wiley Subscription Services, Inc</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QG</scope><scope>7SN</scope><scope>7TN</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H95</scope><scope>L.G</scope><scope>P64</scope><scope>RC3</scope><scope>7X8</scope><orcidid>https://orcid.org/0000-0002-5486-175X</orcidid></search><sort><creationdate>201811</creationdate><title>Decadal‐scale response of detritivorous surgeonfishes (family Acanthuridae) to no‐take marine reserve protection and changes in benthic habitat</title><author>Russ, Garry R. ; Payne, Cody S. ; Bergseth, Brock J. ; Rizzari, Justin R. ; Abesamis, Rene A. ; Alcala, Angel C.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3889-89d2de902a20ccce661acabffc3cfec411cc81db644302b216f7df7817ee1a533</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Acanthuridae</topic><topic>Animals</topic><topic>Anthozoa - physiology</topic><topic>Aquatic habitats</topic><topic>benthic habitat</topic><topic>Catch per unit effort</topic><topic>Conservation of Natural Resources - methods</topic><topic>Coral Reefs</topic><topic>Corals</topic><topic>coral‐reef fish</topic><topic>Cyclonic Storms</topic><topic>Density</topic><topic>detritivores</topic><topic>Disturbances</topic><topic>Ecosystem</topic><topic>environmental disturbance</topic><topic>Environmental effects</topic><topic>Explosives</topic><topic>Fishes - physiology</topic><topic>Fishing</topic><topic>Fishing effort</topic><topic>Fishing pressure</topic><topic>Food availability</topic><topic>Food supply</topic><topic>Habitat changes</topic><topic>Habitats</topic><topic>Hurricanes</topic><topic>Marine invertebrates</topic><topic>Marine parks</topic><topic>no‐take reserves</topic><topic>Philippines</topic><topic>Population Dynamics</topic><topic>Protection</topic><topic>Species</topic><topic>Stress, Physiological</topic><topic>Substrata</topic><topic>Typhoons</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Russ, Garry R.</creatorcontrib><creatorcontrib>Payne, Cody S.</creatorcontrib><creatorcontrib>Bergseth, Brock J.</creatorcontrib><creatorcontrib>Rizzari, Justin R.</creatorcontrib><creatorcontrib>Abesamis, Rene A.</creatorcontrib><creatorcontrib>Alcala, Angel C.</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Animal Behavior Abstracts</collection><collection>Ecology Abstracts</collection><collection>Oceanic Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Journal of fish biology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Russ, Garry R.</au><au>Payne, Cody S.</au><au>Bergseth, Brock J.</au><au>Rizzari, Justin R.</au><au>Abesamis, Rene A.</au><au>Alcala, Angel C.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Decadal‐scale response of detritivorous surgeonfishes (family Acanthuridae) to no‐take marine reserve protection and changes in benthic habitat</atitle><jtitle>Journal of fish biology</jtitle><addtitle>J Fish Biol</addtitle><date>2018-11</date><risdate>2018</risdate><volume>93</volume><issue>5</issue><spage>887</spage><epage>900</epage><pages>887-900</pages><issn>0022-1112</issn><eissn>1095-8649</eissn><abstract>No‐take marine reserves (NTMR) are increasingly being implemented to mitigate the effects of fishing on coral reefs, yet determining the efficacy of NTMRs depends largely on partitioning the effects of fishing from the effect of benthic habitat. Species of coral‐reef fishes typically decline in density when subjected to fishing or benthic disturbances, but this is not always the case. This study documents the long‐term (8–31 years) response of six species of detritivorous surgeonfishes (family Acanthuridae) to NTMR protection and benthic habitat change at four islands (Apo, Sumilon, Mantigue, Selinog) in the central Philippines, each island with a NTMR and a monitored fished site. Despite being subject to moderate fishing pressure, these species did not increase in density with NTMR protection. However, density of these surgeonfishes had a strong negative relationship with cover of live hard coral and a strong positive relationship with cover of dead substratum (sand, rubble, hard dead substratum). These surgeonfishes typically feed over dead substrata and thus probably increase in density following large environmental disturbances that substantially reduce live hard coral cover. Here, we describe effects of environmental disturbance events (e.g., use of explosives, typhoons) that reduced live hard‐coral cover and subsequent large increases (up to 25 fold) in surgeonfish densities, which then slowly (over 5–15 years) decreased in density as live hard coral recovered. Density of these functionally important surgeonfish species was influenced more by changes to benthic cover than by NTMR protection. Thus, we highlight the greater importance of bottom‐up controls (i.e., benthic changes to food availability) than top‐down control (i.e., fishing) on a functionally important group of coral‐reef fishes.</abstract><cop>Oxford, UK</cop><pub>Blackwell Publishing Ltd</pub><pmid>30246331</pmid><doi>10.1111/jfb.13809</doi><tpages>14</tpages><orcidid>https://orcid.org/0000-0002-5486-175X</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | Acanthuridae Animals Anthozoa - physiology Aquatic habitats benthic habitat Catch per unit effort Conservation of Natural Resources - methods Coral Reefs Corals coral‐reef fish Cyclonic Storms Density detritivores Disturbances Ecosystem environmental disturbance Environmental effects Explosives Fishes - physiology Fishing Fishing effort Fishing pressure Food availability Food supply Habitat changes Habitats Hurricanes Marine invertebrates Marine parks no‐take reserves Philippines Population Dynamics Protection Species Stress, Physiological Substrata Typhoons |
title | Decadal‐scale response of detritivorous surgeonfishes (family Acanthuridae) to no‐take marine reserve protection and changes in benthic habitat |
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