Minimizing impacts of maintenance dredged material disposal in the coastal environment: A habitat approach
At present, coastal disposal of maintenance dredged material constitutes one of the most important problems in coastal zone management and in some coastal areas represents the major anthropogenic disturbance to the benthos. In this review we first propose, based on the classic literature, that macro...
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description | At present, coastal disposal of maintenance dredged material constitutes one of the most important problems in coastal zone management and in some coastal areas represents the major anthropogenic disturbance to the benthos. In this review we first propose, based on the classic literature, that macrofaunal communities typical of environmentally stressed habitats are more resilient than those of more environmentally stable habitats, and we outline the macrofaunal successional changes following a disturbance. Second, from a review and analysis of the published and unpublished literature on macrofaunal recovery following maintenance dredged material deposition in the coastal environment, we compare the successional sequences and recovery rates in euhaline and polyhaline systems. The review reveals that invertebrate recovery following dredged material disposal in relatively unstressed marine environments generally takes between 1 and 4 years, while in more naturally stressed areas, recovery is generally achieved within 9 months, although deeper polyhaline habitats can take up to 2 years to recover. Differences in recovery times are attributed to the number of successional stages required to regain the original community composition and that species typical of naturally unstressed assemblages do not possess life-history traits to allow rapid recolonization of disturbances. In the last section of this review, the management implications of these findings are discussed in terms of minimizing dredged material disposal impacts on fisheries resources. Since the natural disturbance regime appears to be very important in determining the response of a benthic community following dredged material disposal, it is recommended that when predicting the potential environmental impact of an operation, the nature of the physical environment in combination with the status (and role) of associated marine benthic communities should be considered. |
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In this review we first propose, based on the classic literature, that macrofaunal communities typical of environmentally stressed habitats are more resilient than those of more environmentally stable habitats, and we outline the macrofaunal successional changes following a disturbance. Second, from a review and analysis of the published and unpublished literature on macrofaunal recovery following maintenance dredged material deposition in the coastal environment, we compare the successional sequences and recovery rates in euhaline and polyhaline systems. The review reveals that invertebrate recovery following dredged material disposal in relatively unstressed marine environments generally takes between 1 and 4 years, while in more naturally stressed areas, recovery is generally achieved within 9 months, although deeper polyhaline habitats can take up to 2 years to recover. Differences in recovery times are attributed to the number of successional stages required to regain the original community composition and that species typical of naturally unstressed assemblages do not possess life-history traits to allow rapid recolonization of disturbances. In the last section of this review, the management implications of these findings are discussed in terms of minimizing dredged material disposal impacts on fisheries resources. Since the natural disturbance regime appears to be very important in determining the response of a benthic community following dredged material disposal, it is recommended that when predicting the potential environmental impact of an operation, the nature of the physical environment in combination with the status (and role) of associated marine benthic communities should be considered.</description><identifier>ISSN: 0364-152X</identifier><identifier>EISSN: 1432-1009</identifier><identifier>DOI: 10.1007/s00267-003-2998-2</identifier><identifier>PMID: 14753644</identifier><identifier>CODEN: EMNGDC</identifier><language>eng</language><publisher>New York, NY: Springer</publisher><subject>Animal, plant and microbial ecology ; Animals ; Anthropogenic factors ; Applied ecology ; Benthic communities ; Benthos ; Biological and medical sciences ; Coastal environments ; Coastal zone ; Coastal zone management ; Community composition ; Conservation of Natural Resources ; Conservation, protection and management of environment and wildlife ; Dredging ; Ecology ; Environmental impact ; Environmental management ; Fishery resources ; Fundamental and applied biological sciences. 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Differences in recovery times are attributed to the number of successional stages required to regain the original community composition and that species typical of naturally unstressed assemblages do not possess life-history traits to allow rapid recolonization of disturbances. In the last section of this review, the management implications of these findings are discussed in terms of minimizing dredged material disposal impacts on fisheries resources. Since the natural disturbance regime appears to be very important in determining the response of a benthic community following dredged material disposal, it is recommended that when predicting the potential environmental impact of an operation, the nature of the physical environment in combination with the status (and role) of associated marine benthic communities should be considered.</description><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Anthropogenic factors</subject><subject>Applied ecology</subject><subject>Benthic communities</subject><subject>Benthos</subject><subject>Biological and medical sciences</subject><subject>Coastal environments</subject><subject>Coastal zone</subject><subject>Coastal zone management</subject><subject>Community composition</subject><subject>Conservation of Natural Resources</subject><subject>Conservation, protection and management of environment and wildlife</subject><subject>Dredging</subject><subject>Ecology</subject><subject>Environmental impact</subject><subject>Environmental management</subject><subject>Fishery resources</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Geologic Sediments</subject><subject>Habitats</subject><subject>Invertebrates</subject><subject>Life history</subject><subject>Marine environment</subject><subject>Population Dynamics</subject><subject>Recolonization</subject><subject>Refuse Disposal</subject><subject>Seawater</subject><issn>0364-152X</issn><issn>1432-1009</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2003</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>8G5</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNqFkUuLFDEQgIMo7uzqD_AiQdBba94Pb8uiq7DiRcFbyCTVOxm6022SEdZfb5YZWPCypzzqq0pVPoReUfKeEqI_VEKY0gMhfGDWmoE9QRsqOBt61D5FG8KVGKhkv87Qea170kFj5HN0RoWWPSY2aP8t5TSnvynf4jSvPrSKlxHPPuUG2ecAOBaItxD7XYOS_IRjqutS-yZl3HaAw-Jr60fIf1JZ8gy5fcSXeOe3qfmG_bqWxYfdC_Rs9FOFl6f1Av38_OnH1Zfh5vv116vLmyEIqtpglCE0eAZCeilHoSNjXEu6NaCMNVFx6yOVgYLdBtB0NIRLziJoO3LjJb9A7451-7O_D1Cbm1MNME0-w3KoTlNJLSGPg0wbRawkj4LUCkq0tR188x-4Xw4l92mdZlZwZZjqED1CoSy1FhjdWtLsy52jxN17dUevruty914d6zmvT4UP2xniQ8ZJZAfengBfg5_G0tWl-sD1H-odWP4PbxmqUQ</recordid><startdate>20030901</startdate><enddate>20030901</enddate><creator>BOLAM, Stefan G</creator><creator>REES, Hubert L</creator><general>Springer</general><general>Springer Nature B.V</general><scope>IQODW</scope><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>3V.</scope><scope>7QL</scope><scope>7RV</scope><scope>7SN</scope><scope>7ST</scope><scope>7T7</scope><scope>7U9</scope><scope>7WY</scope><scope>7WZ</scope><scope>7X7</scope><scope>7XB</scope><scope>87Z</scope><scope>88E</scope><scope>88I</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8FL</scope><scope>8G5</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BEZIV</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FRNLG</scope><scope>FYUFA</scope><scope>F~G</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>H94</scope><scope>HCIFZ</scope><scope>K60</scope><scope>K6~</scope><scope>K9.</scope><scope>L.-</scope><scope>M0C</scope><scope>M0S</scope><scope>M1P</scope><scope>M2O</scope><scope>M2P</scope><scope>M7N</scope><scope>MBDVC</scope><scope>NAPCQ</scope><scope>P64</scope><scope>PATMY</scope><scope>PQBIZ</scope><scope>PQBZA</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>SOI</scope><scope>7TN</scope><scope>7TV</scope><scope>7U6</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>KR7</scope><scope>7X8</scope></search><sort><creationdate>20030901</creationdate><title>Minimizing impacts of maintenance dredged material disposal in the coastal environment: A habitat approach</title><author>BOLAM, Stefan G ; REES, Hubert L</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c416t-86801ca2e45a55f47d223751b8e6898d639ad15c1e9bce71f803532de79f38a53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2003</creationdate><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Anthropogenic factors</topic><topic>Applied ecology</topic><topic>Benthic communities</topic><topic>Benthos</topic><topic>Biological and medical sciences</topic><topic>Coastal environments</topic><topic>Coastal zone</topic><topic>Coastal zone management</topic><topic>Community composition</topic><topic>Conservation of Natural Resources</topic><topic>Conservation, protection and management of environment and wildlife</topic><topic>Dredging</topic><topic>Ecology</topic><topic>Environmental impact</topic><topic>Environmental management</topic><topic>Fishery resources</topic><topic>Fundamental and applied biological sciences. 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Academic</collection><jtitle>Environmental management (New York)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>BOLAM, Stefan G</au><au>REES, Hubert L</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Minimizing impacts of maintenance dredged material disposal in the coastal environment: A habitat approach</atitle><jtitle>Environmental management (New York)</jtitle><addtitle>Environ Manage</addtitle><date>2003-09-01</date><risdate>2003</risdate><volume>32</volume><issue>2</issue><spage>171</spage><epage>188</epage><pages>171-188</pages><issn>0364-152X</issn><eissn>1432-1009</eissn><coden>EMNGDC</coden><abstract>At present, coastal disposal of maintenance dredged material constitutes one of the most important problems in coastal zone management and in some coastal areas represents the major anthropogenic disturbance to the benthos. In this review we first propose, based on the classic literature, that macrofaunal communities typical of environmentally stressed habitats are more resilient than those of more environmentally stable habitats, and we outline the macrofaunal successional changes following a disturbance. Second, from a review and analysis of the published and unpublished literature on macrofaunal recovery following maintenance dredged material deposition in the coastal environment, we compare the successional sequences and recovery rates in euhaline and polyhaline systems. The review reveals that invertebrate recovery following dredged material disposal in relatively unstressed marine environments generally takes between 1 and 4 years, while in more naturally stressed areas, recovery is generally achieved within 9 months, although deeper polyhaline habitats can take up to 2 years to recover. Differences in recovery times are attributed to the number of successional stages required to regain the original community composition and that species typical of naturally unstressed assemblages do not possess life-history traits to allow rapid recolonization of disturbances. In the last section of this review, the management implications of these findings are discussed in terms of minimizing dredged material disposal impacts on fisheries resources. Since the natural disturbance regime appears to be very important in determining the response of a benthic community following dredged material disposal, it is recommended that when predicting the potential environmental impact of an operation, the nature of the physical environment in combination with the status (and role) of associated marine benthic communities should be considered.</abstract><cop>New York, NY</cop><pub>Springer</pub><pmid>14753644</pmid><doi>10.1007/s00267-003-2998-2</doi><tpages>18</tpages></addata></record> |
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subjects | Animal, plant and microbial ecology Animals Anthropogenic factors Applied ecology Benthic communities Benthos Biological and medical sciences Coastal environments Coastal zone Coastal zone management Community composition Conservation of Natural Resources Conservation, protection and management of environment and wildlife Dredging Ecology Environmental impact Environmental management Fishery resources Fundamental and applied biological sciences. Psychology General aspects Geologic Sediments Habitats Invertebrates Life history Marine environment Population Dynamics Recolonization Refuse Disposal Seawater |
title | Minimizing impacts of maintenance dredged material disposal in the coastal environment: A habitat approach |
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