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U.S. Commission on Ocean Policy - Joint Ocean Commission Initiative

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appear to be exacerbating other coral disease outbreaks. 10 Although little is known aboutthe c<strong>on</strong>diti<strong>on</strong> of the world’s deep-water coral communities, extensive damage has beendocumented in some areas, with fishing activities suspected as being the largest humanrelatedthreat. 11Worldwide, no pristine, undamaged warm-water coral reefs remain, and <strong>on</strong>e-third ofthe world’s identified reefs are severely damaged. 12 In the United States, every warm-waterreef system has suffered varying degrees of impacts from natural and human disturbances.Only the coral reefs in the Northwest Hawaiian Islands and some remote Pacific refugesare in near-pristine c<strong>on</strong>diti<strong>on</strong>, although they too have started to show signs of damage,particularly from marine debris. In the U.S. waters of the south Atlantic, Gulf of Mexico,and Caribbean, two-thirds of reef fish species are overfished. In additi<strong>on</strong>, during the 1990s,white band disease killed 90–96 percent of the most comm<strong>on</strong> nearshore species of corals. 13Coral communities have existed for milli<strong>on</strong>s of years and have developed mechanismsto cope with natural threats such as hurricanes, landslides, and predati<strong>on</strong>. Often, when <strong>on</strong>epart of a coral community is damaged, the overall functi<strong>on</strong>ing of the coral reef ecosystem issustained by other, untouched communities that are able to repopulate damaged areas.However, the point is fast approaching where this natural cycle of repair may not be able tokeep pace with the increasing rate of damage. Without immediate and large-scale protecti<strong>on</strong>from the cumulative impacts of a multitude of human activities, many reefs, particularlythose located near heavily populated coastal areas, may so<strong>on</strong> be irretrievably harmed. 14Managing U.S. Coral ResourcesFederal Agency Roles and Resp<strong>on</strong>sibilitiesAlthough a number of l<strong>on</strong>gstanding envir<strong>on</strong>mental laws can be applied to the protecti<strong>on</strong>of coral reefs, the first legislati<strong>on</strong> specifically targeted at coral reef issues, the Coral ReefC<strong>on</strong>servati<strong>on</strong> Act, was passed in 2000. The Act focuses primarily <strong>on</strong> NOAA activities,requiring the agency to develop a nati<strong>on</strong>al coral reef acti<strong>on</strong> strategy, initiate a matchinggrants program for reef c<strong>on</strong>servati<strong>on</strong>, and create a c<strong>on</strong>servati<strong>on</strong> fund to encourage publicprivatepartnerships.The Nati<strong>on</strong>al Marine Sanctuaries Act (NMSA) also provides protecti<strong>on</strong> for many coralreefs by authorizing NOAA to designate areas as marine sanctuaries and promulgate regulati<strong>on</strong>sfor the c<strong>on</strong>servati<strong>on</strong> and management of those areas. Since the Act was passed in1972, thirteen sanctuaries have been designated, several of which c<strong>on</strong>tain coral communities.Coral research, m<strong>on</strong>itoring, and management activities are c<strong>on</strong>ducted in these sanctuaries,as well as in the Reef Ecosystem Reserve, which is currently under c<strong>on</strong>siderati<strong>on</strong>to become the nati<strong>on</strong>’s fourteenth sanctuary.The NMSA includes a provisi<strong>on</strong> that allows NOAA to fund repairs to injured habitatswithin sanctuaries, including coral reefs, with cost recovery from resp<strong>on</strong>sible parties. If adamaged coral reef cannot be restored or replaced, recovered funds may be used to restoreother habitats within the same sanctuary; if neither is possible, restorati<strong>on</strong> efforts may befunded in another nati<strong>on</strong>al marine sanctuary. The statute does not address the use ofrecovered funds for proactive projects designed to prevent injuries before they occur, suchas the installati<strong>on</strong> of navigati<strong>on</strong>al aids to prevent ships grounding <strong>on</strong> coral reefs. Further,the NMSA does not apply to coral reefs outside sanctuaries and does not help in preventingl<strong>on</strong>g-term chr<strong>on</strong>ic damage to corals from polluti<strong>on</strong>, nutrient overloading, or disease.Other federal laws that are used to manage and protect coral reef resources include thefollowing (a descripti<strong>on</strong> of these and other federal statutes are included in Appendix D):• The Magnus<strong>on</strong>–Stevens Fishery C<strong>on</strong>servati<strong>on</strong> and Management Act, which allows formanagement of coral harvest and provides limited protecti<strong>on</strong>s for corals if they aredesignated as “essential fish habitat.”C HAPTER 21: PRESERVING C ORAL R EEFS AND OTHER C ORAL C OMMUNITIES323

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