Establishing Representative No-Take Areas in the Great Barrier Reef: Large-Scale Implementation of Theory on Marine Protected Areas
The Great Barrier Reef Marine Park, an area almost the size of Japan, has a new network of no-take areas that significantly improves the protection of biodiversity. The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature....
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Veröffentlicht in: | Conservation biology 2005-12, Vol.19 (6), p.1733-1744 |
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creator | FERNANDES, LEANNE DAY, JON LEWIS, ADAM SLEGERS, SUZANNE KERRIGAN, BRIGID BREEN, DAN CAMERON, DARREN JAGO, BELINDA HALL, JAMES LOWE, DAVE INNES, JAMES TANZER, JOHN CHADWICK, VIRGINIA THOMPSON, LEANNE GORMAN, KERRIE SIMMONS, MARK BARNETT, BRYONY SAMPSON, KIRSTI DE'ATH, GLENN MAPSTONE, BRUCE MARSH, HELENE POSSINGHAM, HUGH BALL, IAN WARD, TREVOR DOBBS, KIRSTIN AUMEND, JAMES SLATER, DEB STAPLETON, KATE |
description | The Great Barrier Reef Marine Park, an area almost the size of Japan, has a new network of no-take areas that significantly improves the protection of biodiversity. The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature. For example, the new network of no-take areas has at least 20% protection per "bioregion," minimum levels of protection for all known habitats and special or unique features, and minimum sizes for no-take areas of at least 10 or 20 km across at the smallest diameter. Overall, more than 33% of the Great Barrier Reef Marine Park is now in no-take areas (previously 4.5%). The steps taken leading to this outcome were to clarify to the interested public why the existing level of protection was inadequate; detail the conservation objectives of establishing new no-take areas; work with relevant and independent experts to define, and contribute to, the best scientific process to deliver on the objectives; describe the biodiversity (e.g., map bioregions); define operational principles needed to achieve the objectives; invite community input on all of the above; gather and layer the data gathered in round-table discussions; report the degree of achievement of principles for various options of no-take areas; and determine how to address negative impacts. Some of the key success factors in this case have global relevance and include focusing initial communication on the problem to be addressed; applying the precautionary principle; using independent experts; facilitating input to decision making; conducting extensive and participatory consultation; having an existing marine park that encompassed much of the ecosystem; having legislative power under federal law; developing high-level support; ensuring agency priority and ownership; and being able to address the issue of displaced fishers. |
doi_str_mv | 10.1111/j.1523-1739.2005.00302.x |
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The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature. For example, the new network of no-take areas has at least 20% protection per "bioregion," minimum levels of protection for all known habitats and special or unique features, and minimum sizes for no-take areas of at least 10 or 20 km across at the smallest diameter. Overall, more than 33% of the Great Barrier Reef Marine Park is now in no-take areas (previously 4.5%). The steps taken leading to this outcome were to clarify to the interested public why the existing level of protection was inadequate; detail the conservation objectives of establishing new no-take areas; work with relevant and independent experts to define, and contribute to, the best scientific process to deliver on the objectives; describe the biodiversity (e.g., map bioregions); define operational principles needed to achieve the objectives; invite community input on all of the above; gather and layer the data gathered in round-table discussions; report the degree of achievement of principles for various options of no-take areas; and determine how to address negative impacts. Some of the key success factors in this case have global relevance and include focusing initial communication on the problem to be addressed; applying the precautionary principle; using independent experts; facilitating input to decision making; conducting extensive and participatory consultation; having an existing marine park that encompassed much of the ecosystem; having legislative power under federal law; developing high-level support; ensuring agency priority and ownership; and being able to address the issue of displaced fishers.</description><identifier>ISSN: 0888-8892</identifier><identifier>EISSN: 1523-1739</identifier><identifier>DOI: 10.1111/j.1523-1739.2005.00302.x</identifier><language>eng</language><publisher>350 Main Street , Malden , MA 02148 , USA , and 9600 Garsington Road , Oxford OX4 2DQ , UK: Blackwell Science Inc</publisher><subject>Aquatic habitats ; Biodiversity ; biophysical operational principles ; Bioregions ; Conservation biology ; Coral reefs ; cultural operational principles ; economic operational principles ; Environmental policy ; Habitat conservation ; Marine ; Marine conservation ; Marine ecosystems ; Marine protected areas ; principios operacionales biofísicos ; principios operacionales culturales ; principios operacionales culturales,principios operacionales económicos ; principios operacionales económicos ; principios operacionales sociales ; Reefs ; reserve-design software ; social operational principles ; software para diseño de reservas ; Special Section: Implementation and Management of Marine Protected Areas ; Wildlife sanctuaries ; Zoning</subject><ispartof>Conservation biology, 2005-12, Vol.19 (6), p.1733-1744</ispartof><rights>Copyright 2005 Society for Conservation Biology</rights><rights>2005 Society for Conservation Biology</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4842-fcf1a2d2bdffe75a91421c22f2773538caf2e8ade1ea995dae939da624967d953</citedby><cites>FETCH-LOGICAL-c4842-fcf1a2d2bdffe75a91421c22f2773538caf2e8ade1ea995dae939da624967d953</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/3591195$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/3591195$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,776,780,799,1411,27901,27902,57992,58225</link.rule.ids></links><search><creatorcontrib>FERNANDES, LEANNE</creatorcontrib><creatorcontrib>DAY, JON</creatorcontrib><creatorcontrib>LEWIS, ADAM</creatorcontrib><creatorcontrib>SLEGERS, SUZANNE</creatorcontrib><creatorcontrib>KERRIGAN, BRIGID</creatorcontrib><creatorcontrib>BREEN, DAN</creatorcontrib><creatorcontrib>CAMERON, DARREN</creatorcontrib><creatorcontrib>JAGO, BELINDA</creatorcontrib><creatorcontrib>HALL, JAMES</creatorcontrib><creatorcontrib>LOWE, DAVE</creatorcontrib><creatorcontrib>INNES, JAMES</creatorcontrib><creatorcontrib>TANZER, JOHN</creatorcontrib><creatorcontrib>CHADWICK, VIRGINIA</creatorcontrib><creatorcontrib>THOMPSON, LEANNE</creatorcontrib><creatorcontrib>GORMAN, KERRIE</creatorcontrib><creatorcontrib>SIMMONS, MARK</creatorcontrib><creatorcontrib>BARNETT, BRYONY</creatorcontrib><creatorcontrib>SAMPSON, KIRSTI</creatorcontrib><creatorcontrib>DE'ATH, GLENN</creatorcontrib><creatorcontrib>MAPSTONE, BRUCE</creatorcontrib><creatorcontrib>MARSH, HELENE</creatorcontrib><creatorcontrib>POSSINGHAM, HUGH</creatorcontrib><creatorcontrib>BALL, IAN</creatorcontrib><creatorcontrib>WARD, TREVOR</creatorcontrib><creatorcontrib>DOBBS, KIRSTIN</creatorcontrib><creatorcontrib>AUMEND, JAMES</creatorcontrib><creatorcontrib>SLATER, DEB</creatorcontrib><creatorcontrib>STAPLETON, KATE</creatorcontrib><title>Establishing Representative No-Take Areas in the Great Barrier Reef: Large-Scale Implementation of Theory on Marine Protected Areas</title><title>Conservation biology</title><description>The Great Barrier Reef Marine Park, an area almost the size of Japan, has a new network of no-take areas that significantly improves the protection of biodiversity. The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature. For example, the new network of no-take areas has at least 20% protection per "bioregion," minimum levels of protection for all known habitats and special or unique features, and minimum sizes for no-take areas of at least 10 or 20 km across at the smallest diameter. Overall, more than 33% of the Great Barrier Reef Marine Park is now in no-take areas (previously 4.5%). The steps taken leading to this outcome were to clarify to the interested public why the existing level of protection was inadequate; detail the conservation objectives of establishing new no-take areas; work with relevant and independent experts to define, and contribute to, the best scientific process to deliver on the objectives; describe the biodiversity (e.g., map bioregions); define operational principles needed to achieve the objectives; invite community input on all of the above; gather and layer the data gathered in round-table discussions; report the degree of achievement of principles for various options of no-take areas; and determine how to address negative impacts. Some of the key success factors in this case have global relevance and include focusing initial communication on the problem to be addressed; applying the precautionary principle; using independent experts; facilitating input to decision making; conducting extensive and participatory consultation; having an existing marine park that encompassed much of the ecosystem; having legislative power under federal law; developing high-level support; ensuring agency priority and ownership; and being able to address the issue of displaced fishers.</description><subject>Aquatic habitats</subject><subject>Biodiversity</subject><subject>biophysical operational principles</subject><subject>Bioregions</subject><subject>Conservation biology</subject><subject>Coral reefs</subject><subject>cultural operational principles</subject><subject>economic operational principles</subject><subject>Environmental policy</subject><subject>Habitat conservation</subject><subject>Marine</subject><subject>Marine 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biology</jtitle><date>2005-12</date><risdate>2005</risdate><volume>19</volume><issue>6</issue><spage>1733</spage><epage>1744</epage><pages>1733-1744</pages><issn>0888-8892</issn><eissn>1523-1739</eissn><abstract>The Great Barrier Reef Marine Park, an area almost the size of Japan, has a new network of no-take areas that significantly improves the protection of biodiversity. The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature. For example, the new network of no-take areas has at least 20% protection per "bioregion," minimum levels of protection for all known habitats and special or unique features, and minimum sizes for no-take areas of at least 10 or 20 km across at the smallest diameter. Overall, more than 33% of the Great Barrier Reef Marine Park is now in no-take areas (previously 4.5%). The steps taken leading to this outcome were to clarify to the interested public why the existing level of protection was inadequate; detail the conservation objectives of establishing new no-take areas; work with relevant and independent experts to define, and contribute to, the best scientific process to deliver on the objectives; describe the biodiversity (e.g., map bioregions); define operational principles needed to achieve the objectives; invite community input on all of the above; gather and layer the data gathered in round-table discussions; report the degree of achievement of principles for various options of no-take areas; and determine how to address negative impacts. Some of the key success factors in this case have global relevance and include focusing initial communication on the problem to be addressed; applying the precautionary principle; using independent experts; facilitating input to decision making; conducting extensive and participatory consultation; having an existing marine park that encompassed much of the ecosystem; having legislative power under federal law; developing high-level support; ensuring agency priority and ownership; and being able to address the issue of displaced fishers.</abstract><cop>350 Main Street , Malden , MA 02148 , USA , and 9600 Garsington Road , Oxford OX4 2DQ , UK</cop><pub>Blackwell Science Inc</pub><doi>10.1111/j.1523-1739.2005.00302.x</doi><tpages>12</tpages></addata></record> |
fulltext | fulltext |
identifier | ISSN: 0888-8892 |
ispartof | Conservation biology, 2005-12, Vol.19 (6), p.1733-1744 |
issn | 0888-8892 1523-1739 |
language | eng |
recordid | cdi_proquest_miscellaneous_20198940 |
source | Jstor Complete Legacy; Wiley Online Library Journals Frontfile Complete |
subjects | Aquatic habitats Biodiversity biophysical operational principles Bioregions Conservation biology Coral reefs cultural operational principles economic operational principles Environmental policy Habitat conservation Marine Marine conservation Marine ecosystems Marine protected areas principios operacionales biofísicos principios operacionales culturales principios operacionales culturales,principios operacionales económicos principios operacionales económicos principios operacionales sociales Reefs reserve-design software social operational principles software para diseño de reservas Special Section: Implementation and Management of Marine Protected Areas Wildlife sanctuaries Zoning |
title | Establishing Representative No-Take Areas in the Great Barrier Reef: Large-Scale Implementation of Theory on Marine Protected Areas |
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