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Overdue reforms to ocean governance Jon Nevill [email protected] 18 October 2007 It is a widely held view that governance, not science, remains the weakest link in the fishery management chain (Mooney-Seus & Rosenberg 2007:vi, Grafton et al. 2006, Browman & Stergiou 2004, Swan & Greboval 2003, Caddy & Cochrane 2001, Sutton 2001), and this is especially true with respect to the high seas. The lead-up discussions for the 2006 round of the United Nations General Assembly (UNGA) began on 2 October 2006 in New York. Amongst the many draft resolutions circulated amongst member States were two of particular importance for the marine environment: the Law of the Sea resolution and the Fisheries resolution. The purpose of this paper is to highlight the parlous state of marine environments and marine governance, and to ask to what extent are urgent long-term governance reforms being progressed by the UNGA process. The paper argues that ‘freedom of the high seas’ is now a major impediment to ocean conservation and sustainable use. The other major impediment relates to the focus of the bulk of marine management globally on harvesting rather than conservation. I argue that the pervasive and long-standing failures of fishery management will remain the rule rather than the exception until fisheries management agencies, both national and regional, are re-badged and re-focused as ‘biodiversity asset management’ agencies. Although relevant globally, this document was written for an Australian audience. Oceans in crisis: The oceans of the world are being severely damaged. According to a United Nations advisory committee (GESAMP 2001): The state of the world’s seas and oceans is deteriorating. Most of the problems identified decades ago have not been resolved, and many are worsening. New threats keep emerging. The traditional uses of the seas and coasts – and the benefits that humanity gets from them – have been widely undermined. Overfishing, far from being a modern phenomenon, has been occurring in certain regions for a considerable time (Lotze et al. 2006). Overfishing has been the rule rather than the exception, even in artisanal fisheries. As Jackson (2001) points out: “Untold millions of large fishes, sharks, sea turtles and manatees were removed from the Caribbean in the 17 th to 19th centuries. Recent collapses of reef corals and seagrasses are due ultimately to the losses of these large consumers as much as to more recent changes in climate, eutrophication, or outbreaks of disease.” According to Pauly et al. (2002): “Fisheries have rarely been ‘sustainable’. Rather, fishing has induced serial depletions, long masked by improved technology, geographic expansion and exploitation of previously spurned species lower in the food web”. The disturbingly high rate of fishery collapse has not improved over recent years (Mullon et al. 2005). Continuing disregard by fishery managers of scientific advice has been common-place (Murawski 2001). Populations of ocean fishes have been hugely reduced over the last two centuries. Historical evidence suggests that earlier stocks may have been an order of magnitude 1 greater than stocks in the last half-century (Steele and Schumacher 2000) – which themselves have now often been reduced by another order of magnitude. According to Jackson (2001): “Ecological extinction caused by overfishing precedes all other pervasive human disturbance to coastal ecosystems, including pollution, degradation of water quality, and anthropogenic climate change”. Duda & Sherman (2002) express similar concerns: “Continued over-fishing in the face of scientific warnings, fishing down food webs, 1 destruction of habitat, and accelerated pollution loading especially nitrogen export have resulted in significant degradation to coastal and marine ecosystems of both rich and poor nations.” Subsidization of national fishing fleets continues, in spite of warnings by scientists (eg: Pauly 1995) and the FAO2 (www.fao.org) that excessive fishing pressures are the primary cause of fisheries collapse. Global fishing fleets are two or three times the size necessary to harvest the approximate reported annual global catch of around 100 million tonnes. Many fisheries have “staggering levels of discarded bycatch” which, when combined with unreported, unregulated and illegal fishing, pushes the true global annual catch to around 150 million tonnes (Pauly & Christensen 1995). These figures, although a decade old, are still roughly accurate if Chinese reports of fishing take are adjusted for expected error. Governance failures: As Botsford et al. (1997) pointed out, it is abundantly clear that, at a global level, “[fishery] management has failed to achieve a principal goal, sustainability”. The application of the ecosystem and precautionary approaches have been widely advocated since the early 1980s, and consolidated in international soft law in 1995 through the FAO Code of Conduct for Responsible Fisheries. The Code of Conduct was explicitly endorsed by 124 nations (including Australia) through the Rome Declaration 1999. In hard law, the UN Fish Stocks Agreement 1995 applied these approaches to straddling and migratory fish stocks. The first marine protected areas were created over 100 years ago. While their fishery benefits remain the subject of much discussion and differing views, the value of networks of marine protected areas for biodiversity conservation is now widely recognised within the marine science community. However, in spite of considerable discussion and enthusiasm on the part of practitioners, and endorsement through international soft law, these areas still occupy only a minute fraction of the ocean 3 (virtually all within national EEZs). While it can be argued that some parts of the high seas are protected, the weakness of these protective mechanisms has so far prevented such areas being listed on the World Database of Protected Areas. The high seas, and their protection, remain ‘someone else’s problem’. Considerable guidance is now available on the application of the ecosystem and precautionary approaches to fishery management – through FAO guidelines and conference proceedings, through papers in the scientific press, and even through explicit inclusion of recommended approaches in the addendum to the UN FSA. The UN Convention on the Law of the Sea (UNCLOS) substantially modified the prior doctrine of ‘freedom of the high seas’, partly by the EEZ framework, and partly by defining broad responsibilities accompanying the new rights created within the EEZ framework. However, while EEZ rights have been enthusiastically endorsed by nation-States, the environmental responsibilities defined by UNCLOS have been substantially ignored within EEZs, and almost completely ignored on the high seas. This is the case in spite of the provisions of the Convention on Biological Diversity, the UN FSA, the resolutions of Rio and Johannesburg, and the FAO Code of Conduct. Nations around the world are attempting to respond to these concerns. Fishery management within national EEZs is improving where nations are beginning to develop management regimes incorporating ecosystem and precautionary approaches, and where effective compliance monitoring and enforcement programs are being developed. Smaller third world States have understandable problems in this respect. The high seas remain, however, largely without effective regulation, and fishing operators forced out of EEZs by increasingly restrictive national fishery regimes have been able to continue to operate under flags of convenience. The freedom of the high seas provides unregulated fishing vessels with a golden opportunity. As industry spokesman Martin Exel (Austral Fisheries) puts it: “Until the high seas are managed they will remain sinkholes for 2 unregulated and unreported fishing, and that is unacceptable in this day and age of knowledge and understanding of our oceans”. Regional fisheries management organisations (RFMOs) have, for the most part, been ineffective, with little attempt to apply precautionary or ecosystem approaches, or even to monitor and enforce their own fishery rules. For example a recent FAO report indicated that, although several regional fishery management organisations claimed to be using a precautionary approach, only two (CCAMLR and NASCO) could actually name precautionary elements in their management framework (FAO 2005). This same report (in an assessment of implementation of Article 8 of the Code of Conduct – dealing in part with environmental protection responsibilities) found that about 30 percent of the responding RFMOs indicated that they “had not yet taken steps to ensure that only fishing operations in accordance with the fisheries management measures adopted were conducted within their areas of competence”. Considering that only about half of the world’s RFMOs responded to the FAO survey, this suggests that most RFMOs have yet to implement effective compliance monitoring and surveillance regimes. Amongst fishery managers and marine scientists, there is a general consensus that “governance, not science, remains the weakest link in the management chain” (Browman & Stergiou 2004:270). In spite of the urgency of the situation, several important reforms put forward at the FAO FSA Review Conference (2006) did not achieve consensus, resulting in marginal progress in strengthening or widening the provisions of what is perhaps the most important international hard law in the fisheries area (Beintema et al. 2006). It is time now to consider further major restrictions on freedoms which are being widely abused, to the great detriment of the planet and its inhabitants. The path not taken: Einstein is often quoted as saying that the most difficult problems of today cannot be solved through the same thinking which created them. This is very much the case with the high seas, where the very concept of MPAs rests on the premise that most of the ocean is at risk - and this in turn rests on the historic acceptance of freedom of the seas and the freedom to fish. This is the thinking we need to confront and change. Who benefits by these freedoms today? Martin Exel recently said that legitimate fishing companies want governments to manage the high seas, and that freedom of the seas primarily benefits unregulated fishers, operating under flags of convenience. In theory, political pressure (through the UN) could be put on nations offering flags of convenience, but this course of action has been discussed for decades with little significant progress. It is becoming increasingly obvious Exel’s point is legitimate and important – the freedom of the high seas benefits only pirates, scoundrels, and other IUU fishers. Yet in a recent document, the Australian Government stated: "We support the freedoms of the high seas, but recognise that States have obligations to protect and preserve the marine environment..." As a nation, I believe that Australia needs to take a different line - one that increasingly suggests that these freedoms need to be replaced with an effective international governance regime. Where do we need to go in the long term? Sylvia Earle (echoing the concerns of marine scientists and conservation biologists worldwide 4) has said: "We must place biodiversity conservation at the center of ocean governance." (Earle & Laffoley 2006). This is the crucial point. And governance of the high seas is a necessary condition before biodiversity can be protected and resources managed in a sustainable way. The resources of the deep ocean floor, under the terms of the Law of the Sea, are seen as the ‘common heritage of mankind’. Russ & Zeller (2003) have argued, I believe persuasively, that this concept needs to be extended to the entire high seas ocean, not just the sea floor. They suggest that the high seas should be zoned and managed, and that fishing in these zones, now often seen as a right, should become a privilege, mandated through enforced conditions. This may seem a large step from the current governance arrangements – but perhaps this is more an appearance than a reality. Most of the high seas now fall under the 3 (admittedly often ineffective) governance of regional fisheries management organizations. In fact it may not be such a major step to strengthen these agencies and expand their scope. Government wildlife agencies in many countries have, over long periods, undergone important name changes and changes in focus. In Victoria (Australia), for instance, the late 19th century "Department of Hunting and Game" evolved into the 20th century "Department of Wildlife" which is now part of a large "Department of Sustainability and Environment". The activities and priorities of a department, and the culture of its staff, are importantly shaped by department name, charter and statutory focus – which in this example has evolved from a harvesting charter to a conservation charter. Fishery Departments around the world have not evolved in the same way, to the great detriment of marine biodiversity, and, in many cases, to the great detriment of the fisheries themselves. We need to be pushing the Australian Government towards a future which will see Fishery Departments replaced by Ocean Conservation Departments, where biodiversity conservation is placed at the centre of their statutory charters. And the Australian Government in turn needs to be pushing the United Nations General Assembly, and through the UNGA, the wider global community. The CCAMLR convention5 is the best model we have in the world today for this fundamental change in outlook, partly due to the embodiment of the precautionary and ecosystem approaches into its charter (Constable et al. 2000). While certainly not faultless, the Commission is by far the most effective RFMO globally. Yet (and again this is the point) it is not an RFMO, it is a organisation focussed on conservation. It is an "ocean conservation agency" and a model for the growth of "regional ocean conservation agencies" throughout the world. Article 2 of the Convention states: "The objective of this Convention is the conservation of Antarctic marine living resources. For the purposes of this Convention, the term ‘conservation’ includes rational use." As already mentioned, the convention rests explicitly on the principles of ecosystem-based management and precaution, with a requirement that these principles must be applied, monitored and reported. As a consequence, the whole of the CCAMLR area, vast as it is, technically meets the IUCN criteria for a class IV protected area (putting aside for a moment the issue of non-member State fishing). However, this issue put aside is in fact the broken thread on which the entire global marine governance framework is unravelling – and will continue to unravel in spite of the best intentions of marine scientists, managers and lawyers around the world. The Vienna Convention on the Law of Treaties 1969 establishes a principle that a nationState cannot be bound by international law which it has not, at an earlier time, agreed to. Within the CCAMLR area, there are currently at least as many fishing vessels flagged to non-member States as there are ‘legitimate’ fishing vessels flagged to member States. CCAMLR estimates that around half of the annual take from their area goes to IUU fishers (illegal, unreported or unregulated fishing vessels). Most of these vessels are in fact operating under flags of convenience. Increasingly, the IUU fishing industry is using vessels purpose-built to operate under the flags of nations which do not support CCAMLR, the UN FSA, or any other RFMO (Gianni & Simpson 2005). Four factors combine to provide a recipe for ineffective management and the inevitable slide of marine ecosystems into deeper crisis: the freedom to fish the high seas, still endorsed by UNCLOS; the provisions of the Vienna Convention; the willingness of some nations to put short-term (and relatively small) economic gains ahead of important principles of international cooperation and ecosystem management; and the financial incentives driving the IUU industry. 4 The UN FSA attempts to moderate the provisions of the Vienna Convention by allowing boarding and inspection rights over non-member State vessels. While to be applauded, this approach has not yet been successful in assisting the establishment of a workable governance framework over high seas fish stocks. These provisions were also the subject of heated debate between member and non-member participants at the recent FSA Review Conference (Beintema et al. 2006). Conclusion: Two major changes are necessary to address the current crisis: The first change is to revoke the “freedom to fish” on the high seas and replace it with absolute accreditation rights vested in authoritative regional bodies (such as RFMOs or CCAMLR). In other words, only vessels accredited by the regional bodies would have a legal right to fish in the areas under the jurisdiction of these bodies. The second change is to re-name and re-direct existing RFMOs along the lines of the CCAMLR model, so that they become regional high seas ocean conservation agencies, not regional fishery management organisations as they are now. Although these changes are obvious to many within the marine fraternity (and the first has been advocated by some fishing industry representatives 6 for many years) they represent major shifts in thinking from current governance frameworks. They are not being discussed widely within mainstream international law circles. The negotiations which took place in early 2006 within the frameworks of the UN FSA Review Conference and the Conference of the Parties to the Convention on Biological Diversity have not addressed these issues in outcome statements, although undoubtedly they featured in verbal discussions. The International Seabed Authority (created under the provisions of UNCLOS) provides another model for international governance beyond areas of national jurisdiction. The ISA is founded on the essential principle that the resources of the sea bed are “the common heritage of mankind”. While focussed on utilisation, principles of equity between nations, and sustainability are also embodied in the Authority’s charter. These changes need to be backed up by political will. The financial incentives behind the IUU fishing industry must be removed. A combination of satellite surveillance, catch documentation schemes, port State and flag State controls, and provisions for the seizure of the financial assets of those funding the industry, could be very effective if widely applied. As mentioned above, two resolutions are of particular importance in the coming UNGA meeting in October-November 2006. The UNGA sent the Coordinators First Draft of the Fisheries Resolution to States for comment on the 25th of August 2006. In my view, although in many respects comprehensive, it entirely fails to promote the evolution in governance which is so desperately needed. It rests, in Einstein's words, on the thinking that has created the problems. And, unless fishing agencies and conservation agencies push their States to move towards this evolution, nothing will change. The UNGA is the most appropriate vehicle to promote this change, and we have an opportunity now. Unless this matter is raised at the UNGA discussions scheduled to commence in New York on 2 October 2006, the opportunity to promote gradual (but vital) change will have been lost for this annual cycle of the negotiations. Acknowledgements: Graeme Kelleher (IUCN); Martin Exel (Austral Fisheries); Alistair Graham (WWF Australia). 5 References: Baum, JK & Myers, RA (2004) 'Shifting baselines and the decline of pelagic sharks in the Gulf of Mexico', Ecology Letters, vol. 7, pp. 135-45. Beintema, N, Brooke, A, Hajjar, R & Morgera, E (2006), Summary of the UN Fish Stocks Agreement Review Conference 22-26 May 2006, International Institute for Sustainable Development Earth Negotiations Bulletin, New York. Botsford, LW, Castilla, JC & Peterson, CH (1997) 'The management of fisheries and marine ecosystems', Science, vol. 277, p. 509. Browman, HI & Stergiou, KI (2004) 'Introduction to the theme section: Perspectives on ecosystem-based approaches to the management of marine resources', Marine Ecology Progress Series, vol. 274, pp. 269-303. Caddy, JF & Cochrane, KL (2001) 'A review of fisheries management past and present and some future perspectives for the third millennium', Ocean & Coastal Management, vol. 44, pp. 653-82. Constable, A (2006) 'International implementation of the ecosystem approach to achieve the conservation of Antarctic marine living resources', paper presented to the United Nations Informal Consultation Process on the Law of the Sea, seventh meeting. Constable, A, de la Mare, WK, Agnew, DJ, Everson, I & Miller, D (2000) 'Managing fisheries to conserve the Antarctic marine ecosystem: practical implications of the Convention on the Conservation of Antarctic Marine Living Resources (CCAMLR)', ICES Journal of Marine Sciences, vol. 57, pp. 778-91. Dayton, PK (1998) 'Reversal of the burden of proof in fisheries management', Science, vol. 279, pp. 821-2. Duda, AM & Sherman, K (2002) 'A new imperative for improving management of large marine ecosystems.' Ocean and Coastal Management., vol. 45, no. 11, pp. 797-833. Earle, SA & Laffoley, D (2006) 'Protecting the Earth's last frontier', International Herald Tribune, no. February 19, 2006. FAO (2005), Progress in the implementation of the Code of Conduct for Responsible Fisheries and related Plans of Action, UN Food and Agriculture Organisation, Rome. GESAMP Joint Group of Experts on the Scientific Aspects of Marine Environmental Protection (2001), A sea of troubles, UN Advisory Committee on Protection of the Sea (ACOPS), London. Gianni, M & Simpson, W (2005), The changing nature of high seas fishing: how flags of convenience provide cover for illegal, unreported and unregulated fishing, Department of Agriculture, Fisheries and Forestry, Canberra. Grafton, Q, Kompas, T, McLoughlin, R & Rayns, N (2006) Benchmarking for fisheries governance, Australian National University Economics and Envrionment Network, viewed 3 March 2008. Jackson, JBC (2001a) 'What was natural in the coastal oceans?' Proceedings of the National Academy of Sciences USA, vol. 98, no. 10, pp. 5411-8. Jackson, JBC, Kirby, MX, Berger, WH, Bjorndal, KA, Botsford, LW, Bourque, BJ, Bradbury, RH, Cooke, RG, Erlandson, J, Estes, JA, Hughes, TP, Kidwell, S, Lange, CB, Lenihan, HS, Pandolfi, JM, Peterson, CH, Steneck, RS, Tegner, MJ & Warner, RR (2001b) 'Historical overfishing and the recent collapse of coastal ecosystems.' Science, vol. 293, pp. 629-38. Lotze, HK, Lenihan, HS, Bourque, BJ, Bradbury, RH, Cooke, RG, Kay, MC, Kidwell, S, Kirby, MX, Peterson, CH & Jackson, JBC (2006) 'Depletion, degradation and recovery potential of estuaries and coastal seas', Science, vol. 312, pp. 1806-9. Malakoff, D (1997) 'Extinction on the high seas.' Science, vol. 227, pp. 486-8. Mooney-Seus, ML & Rosenberg, AA (2007) Regional Fisheries Management Organizations (RFMOs): Progress in Adopting the Precautionary Approach and Ecosystem-Based Management, Fort Hill Associates LLC, Rome. 6 Mullon, C, Freon, P & Cury, P (2005) 'The dynamics of collapse in world fisheries', Fish and Fisheries, vol. 6, pp. 111-20. Murawski, SA (2001), Ecosystem-based fishery management: testimony to the subcommittee on fisheries conservation, wildlife and oceans, National Marine Fisheries Service, Washington DC. Myers, RA & Worm, B (2003) 'Rapid worldwide depletion of predatory fish communities', Nature, vol. 423, pp. 280-3. Pauly, D & Christensen, V (1995) 'Primary production required to sustain global fisheries', Nature, vol. 374, no. 6519, pp. 255-7. Pauly, D (1995) 'Anecdotes and the shifting baseline syndrome of fisheries', Trends in Ecology and Evolution, vol. 10, p. 430. Pauly, D, Christensen, V, Guenette, S, Pitcher, TJ, Sumaila, UR, Walters, CJ, Watson, R & Zellar, D (2002) 'Towards sustainability in world fisheries', Nature, vol. 418, pp. 68995. Russ, GR & Zeller, DC (2003) 'From Mare Liberum to Mare Reservarum', Marine Policy, vol. 27, no. 1, pp. 75-8. Sutton, M (2001) 'Harnessing market forces and consumer power in favour of sustainable fisheries', in TJ Pitcher, PJB Hart & D Pauly (eds), Reinventing fisheries management, Kluwer, London. Steele, JH & Schumacher, M (2000) 'Ecosystem structure before fishing', Fisheries Research, vol. 44, no. 3, pp. 201-5. Swan, J & Greboval, D (eds) (2003) Report and documentation of the International Workshop on the Implementation of International Fisheries Instruments and Factors of Unsustainability and Overexploitation in Fisheries. Mauritius, 3-7 February 2003, FAO Fisheries Report. No. 700. Rome, FAO. 2003. 305p. Worm, B, Sandow, M, Oschlies, A, Lotze, HK & Myers, RA (2005) Global patterns of predator diversity in the open oceans, Science Online, viewed 28 July 2005, <www.sciencemag.org/cgi/content/abstract/1113399>. Endnotes: Used here, the term ‘order of magnitude’ means approximately a factor of ten. FAO: the United Nations Food and Agriculture Organization, based in Rome. 3 Marine protected areas listed on the World Database on Protected Areas (www.unepwcmc.org) account for less than 2% of ocean area, while fully protected areas (no-take) account for less than 0.2%. 4 See, for example, comments like those of Dr Bill Ballantine (Leigh Marine Laboratory NZ): “The main challenge facing MPAs is to make the concept redundant as soon as possible” (MPA News October 2005, p.3). 5 CCAMLR: Convention for the Conservation of Antarctic Marine Living Resources 1980. 6 Martin Exel (Austral Fisheries) pers. comm. 10 September 2006. The concept is also advocated by fisheries scientists such as Constable (2006). 1 2 7