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<title lang=en>Great Barrier Reef No-Take Areas Include a Range of Disturbance Regimes</title>
<creator>Maynard, Jeffrey A</creator>
<creator>Beeden, Roger</creator>
<creator>Puotinen, Marjetta</creator>
<creator>Johnson, Johanna E.</creator>
<creator>Marshall, Paul</creator>
<creator>van Hooidonk, Ruben</creator>
<creator>Devlin, Michelle</creator>
<creator>Lawrey, Eric</creator>
<creator>Dryden, Jen</creator>
<creator>Ban, Natalie</creator>
<creator>Wachenfeld, David</creator>
<creator>Planes, Serge</creator>
<contributor>Centre de recherches insulaires et observatoire de l'environnement (CRIOBE) ; Université de Perpignan Via Domitia (UPVD) - École pratique des hautes études (EPHE) - Centre National de la Recherche Scientifique (CNRS)</contributor>
<contributor>Laboratoire d'Excellence CORAIL (LabEX CORAIL) ; Institut de Recherche pour le Développement (IRD) - Université des Antilles et de la Guyane (UAG) - École des hautes études en sciences sociales (EHESS) - École pratique des hautes études (EPHE) - Institut Français de Recherche pour l'Exploitation de la Mer (IFREMER) - Université de la Réunion (UR) - Université de la Polynésie Française (UPF) - Université de Nouvelle Calédonie - Institut d'écologie et environnement</contributor>
<contributor>Marine Applied Research Center</contributor>
<contributor>Great Barrier Reef Marine Park Authority (GBRMPA)</contributor>
<contributor>College of Marine and Environmental Sciences ; James Cook University (JCU)</contributor>
<contributor>Australian Institute of Marine Science (AIMS)</contributor>
<contributor>C2O Consulting</contributor>
<contributor>Reef Ecologic</contributor>
<contributor>Centre for Biodiversity and Conservation Research ; The University of Queensland [Brisbane]</contributor>
<contributor>NOAA Atlantic Oceanographic and Meteorological Laboratory (AOML) ; National Oceanic and Atmospheric Administration (NOAA)</contributor>
<contributor>Cooperative Institute for Marine and Atmospheric Studies ; University of Miami [Coral Gables]</contributor>
<contributor>School of Environmental Studies ; University of Victoria [Canada] (UVIC)</contributor>
<description>International audience</description>
<source>ISSN: 1755-263X</source>
<source>Conservation Letters</source>
<publisher>Wiley</publisher>
<identifier>hal-01225201</identifier>
<identifier>https://hal-univ-perp.archives-ouvertes.fr/hal-01225201</identifier>
<identifier>https://hal-univ-perp.archives-ouvertes.fr/hal-01225201/document</identifier>
<identifier>https://hal-univ-perp.archives-ouvertes.fr/hal-01225201/file/Maynard_et_al-2015-Conservation_Letters.pdf</identifier>
<source>https://hal-univ-perp.archives-ouvertes.fr/hal-01225201</source>
<source>Conservation Letters, Wiley, 2015, 〈10.1111/conl.12198〉</source>
<identifier>DOI : 10.1111/conl.12198</identifier>
<relation>info:eu-repo/semantics/altIdentifier/doi/10.1111/conl.12198</relation>
<language>en</language>
<subject lang=en>Coral reefs</subject>
<subject lang=en>climate change</subject>
<subject lang=en>exposure</subject>
<subject lang=en>management</subject>
<subject lang=en>marine protected areas</subject>
<subject lang=en>spatial planning</subject>
<subject lang=en>vulnerability</subject>
<subject>[SDE.BE] Environmental Sciences/Biodiversity and Ecology</subject>
<type>info:eu-repo/semantics/article</type>
<type>Journal articles</type>
<description lang=en>Exposure to disturbance is rarely considered in marine protected area planning. Typically, representing and replicating the habitat types present within protected areas is used to spread the risk of protecting frequently disturbed sites. This was the approach used during the 2004 re-zoning of the Great Barrier Reef Marine Park (GBRMP) via the Representative Areas Program. Over 10 years later, we examine whether the risk was spread by mapping exposure of coral reefs in the GBRMP to four disturbances that cause coral mortality: bleaching, tropical cyclones, crown-of-thorns starfish outbreaks, and freshwater inundation. Our objectives were to: (1) assess whether no-take areas include a range of disturbance regimes, and (2) identify coral reef areas with lower relative exposure. At least 13% and an average of 31% of reef locations in each of 11 exposure classes are included within no-take areas. A greater proportion of low-exposure areas are within no-take areas than high-exposure areas (34.2% vs. 28.3%). The results demonstrate the value of risk spreading when exposure data are not available while also showing that regularly assessing exposure increases capacity for adaptive, resilience-based reef management.</description>
<rights>http://creativecommons.org/licenses/by/</rights>
<date>2015-09</date>
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