1. Summary<strong>Marine</strong> reserves, areas permanently closed to all fishing, are frequently proposed as a tool for managingfisheries. Fishery benefits claimed for reserves include increases in spawning stock size, animal body size, andreproductive output of exploited species. Reserves are predicted to augment catches through export of offspringto fishing grounds, and spillover of juveniles and adults from reserves to fisheries. Protection of stocks anddevelopment of extended age structures of populations in reserves are argued to offer insurance againstenvironmental variability and management failure. Models also suggest reserves will reduce year-to-yearvariability in catches, and offer greater simplicity of management and enforcement. Reserves are predicted tolead to habitat recovery from fishing disturbance which can also enhance benefits to fisheries.Extensive field research confirms many of these predictions. Reserves worldwide have led to increasesin abundance, body size, biomass and reproductive output of exploited species. Such measures often increasemany times over, sometimes by an order of magnitude or more. Population build up is usually rapid with effectsdetectable within 2-3 years of protection. Increases are often sustained over extended periods, particularly forlonger-lived species and for measures of habitat recovery. Reserves have benefitted species from a widetaxonomic spectrum that covers most economically important taxa, including many species of fish, crustaceans,mollusks and echinoderms.Encouraged by these results, many countries and states have embarked upon initiatives to establishnetworks of marine reserves. However, reserves remain highly controversial among fishers and fishing industrybodies who argue that fishery benefits remain unproven. In the last three years there has been rapid growth in thenumber of cases where fisheries have been shown to benefit from reserves. In this report, we critically analyzethis body of evidence, drawing upon studies of reserves and fishery closures. Fishery managers have long usedfishery closures, areas temporarily closed to fishing for one or more species or to specific fishing gears. They areemployed to help rebuild depleted stocks, reduce gear conflicts, protect vulnerable life stages of exploitedspecies or protect sensitive habitats from damaging gears. Such areas can tell us much about the potential effectsof marine reserves.Fishery benefits from reserves and fishery closures typically develop quickly, in most cases within fiveyears of their creation. Perhaps the most persuasive evidence of fishery effects of reserves comes from changingfishing patterns. In most places where well-respected reserves or fishery closures exist, fishers tend to move theirfishing activities closer to their boundaries. Fishing-the-line, as it is called, allows fishers to benefit fromspillover of animals from reserves to fishing grounds. There are now well-documented cases of spillover frommore than a dozen countries and including a wide range of species. It is more technically demanding to provefishery enhancement through export of offspring on ocean currents. Existing reserves are generally small,making it hard to detect increased recruitment to fisheries at a regional scale. However, there are now severalcases in which export of eggs and larvae have been confirmed, including dramatic enhancement of scallopfisheries in Georges Bank and clam fisheries in Fiji. Small reserves have worked well and repeatedly producelocal benefits. However, regional fisheries enhancement will require more extensive networks of reserves. Someof the most convincing success stories come from places in which between 10 and 35% of fishing grounds havebeen protected. In several cases there is evidence that yields with reserves have risen to higher levels than priorto protection, despite a reduction in the area of fishing grounds. In other cases, smaller reserves have stabilizedcatches from intensively exploited fisheries or slowed existing rates of decline.We describe experiences that prove that success of marine reserves is not contingent on habitat type,geographical location, the kind of fishery involved, or the technological sophistication of management. Reservebenefits are not restricted to habitats like coral reefs, or to artisanal fisheries, as some critics claim. Fisherybenefits have been demonstrated from reserves established in tropical, warm- and cold-temperate waters, and inmany habitats, including coral reefs, rocky reefs, kelp forests, seagrass beds, mangroves, estuaries, softsediments, continental shelves and deep sea. Reserves and fishery closures have worked well for a wide range offisheries, spanning recreational fisheries, artisanal fisheries like those of coral reefs, through small-scalenearshore fisheries for species like lobsters, up to industrial-scale fisheries for animals like flatfish and scallops.They have worked across a similarly broad spectrum of management sophistication, from self-policing bycommitted fishers, through warden patrols to satellite monitoring of distant fishing activities.We now have strong evidence that with the support of local communities, marine reserves offer ahighly effective management tool. However, reserves will only rarely be adequate as a stand-alone managementapproach, although we describe cases where they have worked in the absence of other measures. They will bemost effective when implemented as part of a package of limits on fishing effort, designed to protect exploitedspecies and their habitats.2. Introduction<strong>Marine</strong> reserves are areas of the sea that are permanently closed to all fishing. They have been attracting theattention of conservationists and fishery managers since the mid-1980s when the first studies of their effects6
egan being published. Those studies indicated that protection from fishing could lead to rapid and dramaticchanges in populations and habitats in reserves. As interest in reserves has developed, the number of reviewsgiving evidence for their effects has escalated with new ones being published every few months (PDT 1990,Roberts and Polunin 1991, 1993a, Dugan and Davis 1993, Rowley 1994, Bohnsack 1996, 1998, Attwood et al.1997, Guenette et al. 1998, Murray et al. 1999, Jennings 2000, Crowder et al. 2000, Mosquera et al. 2000,Palumbi 2001, Halpern and Warner 2002, Russ 2002, Polunin 2002, Roberts in press). There have been similarnumbers of books, reports and national assessments devoted to them (e.g. Ballantine 1991, MRTG 1997,Yoklavich 1998, Fujita et al. 1998, Roberts and Hawkins 2000, NRC 2001, Birkeland and Friedlander 2001, toname a few).Previous reviews present compelling evidence that marine reserves are effective conservation tools.Throughout the world they have had remarkably consistent effects. Protection from fishing leads to rapid buildupof abundance and biomass of populations of exploited species, increases average body size, and extendspopulation age structure. It also increases species diversity, fosters habitat recovery from fishing disturbances,and allows the development of assemblages of species and habitats that are different from those in exploitedareas (for examples see Roberts and Hawkins 2000, NRC 2001, Halpern and Warner 2002, Halpern 2003).The predicted benefits of reserves for adjacent fisheries depend on reserves protecting spawning stocksand vulnerable life stages. In short, protection from fishing allows exploited species to live longer, grow largerand become more numerous, all of which increase reproductive output. Since most exploited marine specieshave pelagic egg or larval stages (Palumbi 2001, Shanks et al. 2003), the offspring of protected animals can bedispersed widely from reserves to re-supply fishing grounds. Furthermore, as stocks build up in reserves, there ispredicted to be movement of juveniles and adults from protected areas to fishing grounds, termed ‘spillover’(Bohnsack 1998). At the management level, reserves are predicted to be simpler and easier to implement incomplex multispecies fisheries than single species approaches (PDT 1990). Models predict that populations inreserves will provide insurance against management failure in surrounding fishing grounds (Lauck et al. 1998),and that reserves will reduce year-to-year variability in catches, making management easier and fishers’ incomesmore predictable (Sladek Nowlis and Roberts 1999). Given the declining state of many of the world’s fisheries,and the seeming inability of present management approaches to prevent decline (Roberts 1997, 2000a, NRC1999), the possible fishery management benefits of reserves have been attracting great interest.Evidence for the success of marine reserves has led to growing efforts to establish more of themworldwide. The Philippines has more than 40 reserves that are well protected and hundreds more have beenestablished there (Pajaro et al. 1999). The State of Victoria in Australia declared 13 marine reservesencompassing 5.3% of state waters in 2002 (http://www.nre.vic.gov.au/). In 1998 the Galapagos Islands ofEcuador were declared a marine park that encompasses 133,000km 2 of ocean. Eighteen percent of the coastlineis included in marine reserve zones closed to fishing (http://www.darwinfoundation.org/marine/zoning.html). Inthe United States, two expert panels of the National Research Council have recommended marine reserves beused widely to protect species, habitats and help sustain fisheries (NRC 1999, 2001). President Clinton issued anExecutive Order in May 2000 charging his agencies to begin developing a national system of marine protectedareas of which a significant part would be protected from all fishing (NRC 2001). The state of California iscurrently embarked upon a process to create a network of marine reserves in state waters.As efforts to set up reserves gather pace, claims for their benefits to fisheries are coming underintensive scrutiny. Proposals to establish marine reserves are often met with hostility by fishing communities.Indeed, opposition from fishers is one of the principal barriers to reserve establishment. Fishers are often wary ofreserves because they see them as taking away from their livelihoods rather than contributing to them. Thesenegative perceptions are reinforced by long experience with a growing body of regulations that have failed tohalt fishery declines and fishers are not convinced that reserves will be any different. Sceptical fishers and theirindustry bodies are demanding proof that reserves can deliver fishery benefits before accepting them, whileothers are showing outright hostility towards reserves. For example, in the United States, recreational fishingindustry groups are opposing reserves and supporting a bill being considered by Congress, The Freedom to FishAct, which would greatly limit the ability of regulatory agencies to protect areas from fishing(http://www.freedomtofish.org/f2f/f2f_act/#house).Recently, there has been a burst of new evidence concerning the fishery effects of reserves, warrantingthis review. In it we synthesise this evidence and focus our analyses around a series of questions about reserveperformance frequently asked by fishers and fishery managers. We complement our review with a series of casestudies documenting reserve effects from all over the world. Readers seeking a greater level of detail shouldrefer to them. In preparing these studies we have benefited from the generosity of many researchers who haveshared their latest findings with us. We demonstrate that the case that reserves benefit fisheries has become muchstronger over the last two to three years and fishers and reserve managers can approach reserve implementationwith newfound confidence. People contemplating reserve creation can take heart from the experiences of otherswho are further along in the process. Their experiences prove that reserves can work successfully across a widerange of ecological and socio-economic conditions.7
- Page 1 and 2: The fishery effects ofmarine reserv
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- Page 9 and 10: unprotected area (21.2cm vs 38.1cm)
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- Page 24 and 25: Literature citedAlder, J. (1996) Co
- Page 26 and 27: Fiske, S.J. (1992) Sociocultural as
- Page 28 and 29: Levine, A. (2002) Global partnershi
- Page 30 and 31: Roberts, C.M. and Hawkins, J.P. (20
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- Page 34 and 35: Mean abundance of fish per count100
- Page 36 and 37: 2. Contrasting experiences from the
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- Page 40 and 41: Key points• Very high reef fisher
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- Page 46 and 47: Ballantine, W.J. (1991) Marine rese
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- Page 50 and 51: ReferencesAttwood, C.G. and Bennett
- Page 52 and 53: 5. Lobster fisheries management in
- Page 54 and 55: Rowe, S. and Feltham, G. (2000) Eas
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fishers. At a meeting of fishers an
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7. Marine parks and other protected
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8. Community-based closed areas in
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People are also seeing some species
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9. The Sambos Ecological Reserve, F
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10. The Nosy Atafana Marine Park, n
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11. Mombasa and Kisite Marine Parks
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species that are mobile enough to d
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Emerton and Tessema (2001) looked a
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McClanahan, T.R. and Mangi, S. (200
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Goodridge et al. (1997) collected b
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offshore fishing with tourism, such
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• The SMMA would have been improv
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species decreased in the second fou
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eserve in the form of increased cat
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15. Merritt Island National Wildlif
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Thousand Islands, St Lucie canal an
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is closed to scallop fishing. Ten y