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

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nomic costs to the fishermen and communities involved. The task is complicated by thefact that even short-term hardships can drive fishermen permanently out of business.Ir<strong>on</strong>ically, the resultant pressure to go slow has sometimes led to c<strong>on</strong>tinued overfishing,and l<strong>on</strong>ger-term socioec<strong>on</strong>omic harm. An ecosystem-based management regime inevitablyrequires tough choices, but it will provide a comprehensive c<strong>on</strong>text within which thosechoices may be made.The RFMCs need to participate in a collaborative process to share their c<strong>on</strong>cerns andhelp shape regi<strong>on</strong>al goals and management plans. Because of their experience in dealingwith diverse c<strong>on</strong>stituents and multiple objectives, the Councils will be extremely helpfulin developing a comprehensive ecosystem-based management approach in the regi<strong>on</strong>s.In additi<strong>on</strong> to integrating fishery issues into an overall regi<strong>on</strong>al perspective, the principlesof ecosystem-based management can guide NMFS and the RFMCs in implementing twodifficult provisi<strong>on</strong>s of the Magnus<strong>on</strong>–Stevens Act related to essential fish habitat and bycatch.Essential Fish HabitatAs discussed in Chapter 11, maintaining healthy, functi<strong>on</strong>ing habitats is an essentialelement of an ecosystem-based management approach. The 1996 amendments to theMagnus<strong>on</strong>–Stevens Act included measures designed specifically to protect habitats importantto managed species. Essential fish habitat (EFH) is defined in the Act as “those watersnecessary to fish for spawning, breeding, or growth to maturity” and the RFMCs arerequired to “describe and identify essential fish habitat” for each fishery. However, it is noteasy to determine which habitats are required by fish. With scant legislative guidance andlittle scientific informati<strong>on</strong> available <strong>on</strong> habitat requirements, RFMCs tended to be broadin their designati<strong>on</strong>s.For example, in the case of Atlantic halibut, the New England RFMC designated theentire Gulf of Maine and almost all of Georges Bank as essential. The North Pacific councildesignated almost the entire EEZ below the Arctic Circle as essential for <strong>on</strong>e species oranother. But when everything is special, nothing is. The current methods have resulted inthe designati<strong>on</strong> of so much habitat that the original purpose of identifying areas thatdeserve focused attenti<strong>on</strong> has been lost.Perhaps in recogniti<strong>on</strong> of this, NMFS designated a subset of EFH called “habitat areasof particular c<strong>on</strong>cern.” These areas were defined in 2002 NMFS regulati<strong>on</strong>s as “discreteareas within essential fish habitat that either play especially important ecological roles inthe life cycles of federally managed fish species or are especially vulnerable to degradati<strong>on</strong>from fishing or other human activities.” Less than <strong>on</strong>e percent of the area initially designatedas EFH has been further characterized as habitat areas of particular c<strong>on</strong>cern.Two alternate approaches for determining critical habitat attempt to improve <strong>on</strong> thecurrent <strong>on</strong>e. Both look at habitat from an ecosystem perspective, instead of trying to identifyhabitat necessary for the survival of an individual species. The first approach uses theabundance of juveniles of several commercially important species as indicators of habitatpreference. 19 It then uses a statistical method to locate the smallest total area that c<strong>on</strong>tainsa sufficient amount of preferred habitat for all species of c<strong>on</strong>cern. The sec<strong>on</strong>d approachexpands <strong>on</strong> the first by attempting to link species distributi<strong>on</strong> with specific habitat types. 20Of course, the identificati<strong>on</strong> of important habitats is <strong>on</strong>ly the first step. Rather thanfocusing solely <strong>on</strong> protecting these habitats from fisheries impacts, NOAA should identifythe full range of threats and work with other agencies, as well as with developers, localand state z<strong>on</strong>ing officials, and others, to create management plans that address all theactivities posing serious risks to marine habitats. Ultimately, the process for designatingand managing EFH should result in the protecti<strong>on</strong> of major fish species during vulnerablestages of their life history, while minimizing disrupti<strong>on</strong> to the fishing industry or otheroffshore uses. Like other resource management programs, any approach to protecting EFHneeds to be enforceable and reas<strong>on</strong>ably simple to implement.C HAPTER 19: ACHIEVING S USTAINABLE F ISHERIES297

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