The goal of Fisheries management is to produce sustainable biological, social, and economic benefits from renewable aquatic resources. Fisheries are classified as renewable because the organisms of interest (e.g., fish, shellfish, reptiles, amphibians, and marine mammals) usually produce an annual biological surplus that with judicious management can be harvested without reducing future productivity. Fisheries management employs activities that protect fishery resources so sustainable exploitation is possible, drawing on fisheries science and possibly including the precautionary principle. Modern fisheries management is often referred to as a governmental system of appropriate management rules based on defined objectives and a mix of management means to implement the rules, which are put in place by a system of monitoring control and surveillance. A popular approach is the ecosystem approach to fisheries management. According to the Food and Agriculture Organization of the United Nations (FAO), there are "no clear and generally accepted definitions of fisheries management". However, the working definition used by the FAO and much cited elsewhere is:
The integrated process of information gathering, analysis, planning, consultation, decision-making, allocation of resources and formulation and implementation, with enforcement as necessary, of regulations or rules which govern fisheries activities in order to ensure the continued productivity of the resources and the accomplishment of other fisheries objectives.
- 1 Objectives
- 2 Management mechanisms
- 3 Fisheries law
- 4 Effects of climate change
- 5 Population dynamics
- 6 Ecosystem based fisheries
- 7 Performance
- 8 History
- 9 See also
- 10 References
According to the FAO, fisheries management should be based explicitly on political objectives, ideally with transparent priorities. Political goals can also be a weak part of fisheries management, since the objectives can conflict with each other. Typical political objectives when exploiting a commercially important fish resource are to:
- maximize sustainable biomass yield
- maximize sustainable economic yield
- secure and increase employment
- secure protein production and food supplies
- increase export income
For the most recent several decades, the political goals in fisheries management of commercially important species have been rapidly evolving, primarily driven by (1) a recognition of the response of fish and other target animals to changing climate, (2) new technologies for fishing particularly on the high seas, (3) development of competing policy priorities for aquatic environments leading to a more ecosystem-based approach to fisheries management, and (4) new scientific insights about the processes affecting fish population size and recruitment.
The political objectives operative in recreational fisheries management are often substantially different than those prevalent in commercial fisheries management. For example, catch-and-release regulations are common in some types of recreational fisheries. Thus, biological yield is of less important.
Fisheries objectives need to be expressed in concrete management rules. In most countries fisheries management rules should be based on the internationally agreed, though non-binding, Code of Conduct for Responsible Fisheries, agreed at a meeting of the U.N.'s Food and Agriculture Organization FAO session in 1995. The precautionary approach it prescribes is typically implemented in concrete management rules as minimum spawning biomass, maximum fishing mortality rates, etc. In 2005 the UBC Fisheries Centre at the University of British Columbia comprehensively reviewed the performance of the world's major fishing nations against the Code.
Many countries have set up Ministries/Government Departments, named "Ministry of Fisheries" or similar, controlling aspects of fisheries within their exclusive economic zones. Four categories of management means have been devised, regulating either input/investment, or output, and operating either directly or indirectly:
|Indirect||Vessel licensing||Catching techniques|
|Direct||Limited entry||Catch quota and technical regulation|
Technical means may include:
- prohibiting devices such as bows and arrows, and spears, or firearms
- prohibiting nets
- setting minimum mesh sizes
- limiting the average potential catch of a vessel in the fleet (vessel and crew size, gear, electronic gear and other physical "inputs".
- prohibiting bait
- limits on fish traps
- limiting the number of poles or lines per fisherman
- restricting the number of simultaneous fishing vessels
- limiting a vessel's average operational intensity per unit time at sea
- limiting average time at sea
Systems that use individual transferable quotas (ITQ), also called individual fishing quota limit the total catch and allocate shares of that quota among the fishers who work that fishery. Fishers can buy/sell/trade shares as they choose.
A large scale study in 2008 provided strong evidence that ITQ's can help to prevent fishery collapse and even restore fisheries that appear to be in decline. Other studies have shown negative socio-economic consequences of ITQs, especially on small-sclale fisheries. These consequences include concentration of quota in that hands of few fishers; increased number of inactive fishers leasing their quotas to others (a phenomenon known as armchair fishermen); and detrimental effects on coastal communities.
Elderly maternal fish
Traditional management practices aim to reduce the number of old, slow-growing fish, leaving more room and resources for younger, faster-growing fish. Most marine fish produce huge numbers of eggs. The assumption was that younger spawners would produce plenty of viable larvae.
However, 2005 research on rockfish shows that large, elderly females are far more important than younger fish in maintaining productive fisheries. The larvae produced by these older maternal fish grow faster, survive starvation better, and are much more likely to survive than the offspring of younger fish. Failure to account for the role of older fish may help explain recent collapses of some major US West Coast fisheries. Recovery of some stocks is expected to take decades. One way to prevent such collapses is to establish marine reserves, where fishing is not allowed and fish populations age naturally.
A Fishery Manager's Guidebook issued in 2002 by the FAO advises that a set of working principles should be applied to "highlight the underlying key issues" of fisheries management.": 130  There are 8 principles that should be considered as a whole in order to best manage a fishery. The first principle focuses on the finite nature of fish stocks and how potential yields must be estimated based on the biological constraints of the population.
In a paper published in 2007, Shertzer and Prager suggested that there can be significant benefits to stock biomass and fishery yield if management is stricter and more prompt. This is supported by recent work on the management of North Sea fisheries in accordance with ranges of acceptable fishing, where fishing at the top of the "acceptable" ranges is many times more risky than fishing near the bottom, but delivers only 20% more yield.
Managing fisheries is about managing people and businesses, and not about managing fish. Fish populations are managed by regulating the actions of people. If fisheries management is to be successful, then associated human factors, such as the reactions of fishermen, are of key importance, and need to be understood.
Management regulations must also consider the implications for stakeholders. Commercial fishermen rely on catches to provide for their families just as farmers rely on crops. Commercial fishing can be a traditional trade passed down from generation to generation. Most commercial fishing is based in towns built around the fishing industry; regulation changes can impact an entire town's economy. Cuts in harvest quotas can have adverse effects on the ability of fishermen to compete with the tourism industry.
Effective management of fisheries includes involving all stakeholders in the fishery. To do this successfully, stakeholders need to feel empowered enough to make meaningful contributions to the management process.
Empowerment has a wide application but in this context it refers to a tool that gives people within the fishing communities an opportunity to shape their own future in order to cope with the impacts from large-scale commercial fishing, competition of resources, and other threats that impact fishing communities.
However, there are limits to empowerment in the fisheries management process. Empowerment maintains an involvement on the part of the state in fisheries management and no matter how empowered the other stakeholders are, the success of fisheries isn't possible without the legislative powers, financial resources, educational support, and research the government provides.
This concept is not accepted by all, as some communities and individuals argue that the state should withdraw completely and let the local communities handle their own fishery management based on cultural traditions and established practices. Additionally, others have argued that co-management only empowers the wealthy and powerful which in turn solidifies and validates the already existing inequalities of fisheries management.
Empowerment working as a function of co-management, carried out correctly, will not only enable but it will authorize individuals and communities to make meaningful contributions to fisheries management. It is a mechanism that works in a loop, where an individual gains empowerment and encouragement from being a part of the group and the collective action is only successful because of its empowered individuals. In order to effectively and successfully use empowerment as co-management, it is imperative that study programs, guidelines, reading materials, manuals, and checklists are developed and incorporated into all fisheries management.
Fisheries mismanagement is due, in part, to corruption. Corruption and bribery influence the number of fishing licenses that are distributed and to whom, as well as the negotiation of fishing acccess agreements. There is evidence of industrial fisheries corruption among the Small Island Developing States of the Pacific Ocean as well as the fisheries off the coast of West Africa. In small-scale fisheries, inspectors who are charged with regulating catch are bribed to give advance notice of surprise inspections and to relax enforcement standards. Some standards are not enforced at all due to bribery, while other infractions may result in smaller fines than mandated. Fishing gear seized during an investigation can also be returned in exchange for a bribe. Corruption of small-scale fisheries has been documented in South Africa and Lake Victoria.
According to fisheries scientist Milo Adkison, the primary limitation in fisheries management decisions is the absence of quality data. Fisheries management decisions are often based on population models, but the models need quality data to be effective. He asserts that scientists and fishery managers would be better served with simpler models and improved data.
Fisheries law is an emerging and specialized area of law which includes the study and analysis of different fisheries management approaches, including seafood safety regulations and aquaculture regulations. Despite its importance, this area is rarely taught at law schools around the world, which leaves a vacuum of advocacy and research.
Fisheries legislation on a national level differs greatly between countries : 130  Fisheries may also be managed on an international level. One of the first laws enacted was the "United Nations Convention on the Law of the Sea of 10 December 1982 (LOS Convention)", which entered into force in 1994.: 130  This law set the foundation for all international agreements related to oceans that followed.
Effects of climate change
In the past, changing climate has affected inland and offshore fisheries and such changes are likely to continue. From a fisheries perspective, the specific driving factors of climate change include rising water temperature, alterations in the hydrologic cycle, changes in nutrient fluxes, and relocation of spawning and nursery habitat. Further, changes in such factors would affect resources at all levels of biological organization, including the genetic, organism, population, and ecosystem levels. Understanding how these factors affect fisheries at a more nuanced level stand as challenges that fisheries scientists, across multiple fields, still need to face.
Population dynamics describes the growth and decline of a given fishery stock over time, as controlled by birth, death and migration. It is the basis for understanding changing fishery patterns and issues such as habitat destruction, predation and optimal harvesting rates. The population dynamics of fisheries has been traditionally used by fisheries scientists to determine sustainable yields.
- N1 = N0 + B − D + I − E
where N1 is the number of individuals at time 1, N0 is the number of individuals at time 0, B is the number of individuals born, D the number that died, I the number that immigrated, and E the number that emigrated between time 0 and time 1. While immigration and emigration can be present in wild fisheries, they are usually not measured.
Care is needed when applying population dynamics to real world fisheries. In the past, over-simplistic modelling, such as ignoring the size, age and reproductive status of the fish, focusing solely on a single species, ignoring bycatch and physical damage to the ecosystem, has accelerated the collapse of key stocks.
Ecosystem based fisheries
We propose that rebuilding ecosystems, and not sustainability per se, should be the goal of fishery management. Sustainability is a deceptive goal because human harvesting of fish leads to a progressive simplification of ecosystems in favour of smaller, high turnover, lower trophic level fish species that are adapted to withstand disturbance and habitat degradation.
According to marine ecologist Chris Frid, the fishing industry points to pollution and global warming as the causes of unprecedentedly low fish stocks in recent years, writing, "Everybody would like to see the rebuilding of fish stocks and this can only be achieved if we understand all of the influences, human and natural, on fish dynamics." Overfishing has also had an effect. Frid adds, “Fish communities can be altered in a number of ways, for example they can decrease if particular sized individuals of a species are targeted, as this affects predator and prey dynamics. Fishing, however, is not the sole perpetrator of changes to marine life - pollution is another example [...] No one factor operates in isolation and components of the ecosystem respond differently to each individual factor."
In contrast to the traditional approach of focusing on a single species, the ecosystem-based approach is organized in terms of ecosystem services. Ecosystem-based fishery concepts have been implemented in some regions. In 2007 a group of scientists offered the following "ten commandments":
* Keep a perspective that is holistic, risk-averse and adaptive.
- Maintain an “old growth” structure in fish populations, since big, old and fat female fish have been shown to be the best spawners, but are also susceptible to overfishing.
- Characterize and maintain the natural spatial structure of fish stocks, so that management boundaries match natural boundaries in the sea.
- Monitor and maintain seafloor habitats to make sure fish have food and shelter.
- Maintain resilient ecosystems that are able to withstand occasional shocks.
- Identify and maintain critical food-web connections, including predators and forage species.
- Adapt to ecosystem changes through time, both short-term and on longer cycles of decades or centuries, including global climate change.
- Account for evolutionary changes caused by fishing, which tends to remove large, older fish.
- Include the actions of humans and their social and economic systems in all ecological equations.
Ecosystem modelling software
Ecopath, with Ecosim (EwE), is an ecosystem modelling software suite. It was initially a NOAA initiative led by Jeffrey Polovina, later primarily developed at the UBC Fisheries Centre of the University of British Columbia. In 2007, it was named as one of the ten biggest scientific breakthroughs in NOAA's 200-year history. The citation states that Ecopath "revolutionized scientists’ ability worldwide to understand complex marine ecosystems". Behind this lies two decades of development work by Villy Christensen, Carl Walters, Daniel Pauly, and other fisheries scientists. As of 2010 there are 6000 registered users in 155 countries. Ecopath is widely used in fisheries management as a tool for modelling and visualising the complex relationships that exist in real world marine ecosystems.
The biomass of certain global fish stocks have been allowed to run down. The biomass of many species have now diminished to the point where it is no longer possible to sustainably catch the amount of fish that could be caught. According to a 2008 UN report, titled The Sunken Billions: The Economic Justification for Fisheries Reform, the world's fishing fleets incur a "$US 50 billion annual economic loss" through depleted stocks and poor fisheries management. The report, produced jointly by the World Bank and the UN Food and Agriculture Organization (FAO), asserts that half the world's fishing fleet could be scrapped with no change in catch.
"By improving governance of marine fisheries, society could capture a substantial part of this $50 billion annual economic loss. Through comprehensive reform, the fisheries sector could become a basis for economic growth and the creation of alternative livelihoods in many countries. At the same time, a nation’s natural capital in the form of fish stocks could be greatly increased and the negative impacts of the fisheries on the marine environment reduced."
The most prominent failure of fisheries management in recent times has perhaps been the events that lead to the collapse of the northern cod fisheries. More recently, the International Consortium of Investigative Journalists produced a series of journalistic investigations called Looting the seas. These detail investigations into the black market for bluefin tuna, the subsidies propping up the Spanish fishing industry, and the overfishing of the Chilean jack mackerel.
Fisheries have been explicitly managed in some places for hundreds of years. More than 80 percent of the world's commercial exploitation of fish and shellfish are harvested from natural occurring populations in the oceans and freshwater areas. For example, the Māori people, New Zealand residents for about 700 years, had prohibitions against taking more than what could be eaten and about giving back the first fish caught as an offering to sea god Tangaroa. Starting in the 18th century attempts were made to regulate fishing in the North Norwegian fishery. This resulted in the enactment of a law in 1816 on the Lofoten fishery, which established in some measure what has come to be known as territorial use rights.
"The fishing banks were divided into areas belonging to the nearest fishing base on land and further subdivided into fields where the boats were allowed to fish. The allocation of the fishing fields was in the hands of local governing committees, usually headed by the owner of the onshore facilities which the fishermen had to rent for accommodation and for drying the fish."
In Europe, governmental resource protection-based fisheries management is a relatively new idea, first developed for North European fisheries after the first Overfishing Conference held in London in 1936. In 1957 British fisheries researchers Ray Beverton and Sidney Holt published a seminal work on North Sea commercial fisheries dynamics. In the 1960s the work became the theoretical platform for North European management schemes. In North America, both commercial and recreational fisheries have been actively managed for over 150 years. All U.S. states and Canadian provinces have fisheries agencies and their employees implement state, provincial, and federal laws using a broad suite of tools and procedures for both freshwater and marine fisheries.
After some years away from the field of fisheries management, Beverton criticized his earlier work in a paper given at the first World Fisheries Congress in Athens in 1992. "The Dynamics of Exploited Fish Populations" expressed his concerns, including the way his and Sidney Holt's work had been misinterpreted and misused by fishery biologists and managers during the previous 30 years. Nevertheless, the institutional foundation for modern fishery management had been laid.
A report by Prince Charles' International Sustainability Unit, the New York-based Environmental Defense Fund and 50in10 published in July 2014 estimated global fisheries were adding $270 billion a year to global GDP, but by full implementation of sustainable fishing, that figure could rise by an extra amount of as much as $50 billion.
- Age class structure
- All the Fish in the Sea: Maximum Sustainable Yield and the Failure of Fisheries Management
- Beverton–Holt model
- Community supported fishery
- Fisheries Law Centre
- Illegal, unreported and unregulated fishing
- International inspection pennant
- List of harvested aquatic animals by weight
- Marine conservation
- Marine Protected Area
- Maximum sustainable yield
- North Pacific Fishery Management Council
- Regional Fisheries Management Organisation
- Sustainable fisheries
- The Sunken Billions
- The End of the Line – documentary
- U.S. Regional Fishery Management Councils
- Western Pacific Regional Fishery Management Council
- Lackey, Robert; Nielsen, Larry, eds. (1980). Fisheries management. Blackwell. p. 422. ISBN 978-0632006151.
- Garcia SM, Zerbi A, Aliaume C, Do Chi T, Lasserre G (2003). The ecosystem approach to fisheries. Issues, terminology, principles, institutional foundations, implementation and outlook. FAO.
- FAO (1997) Fisheries Management Section 1.2, Technical Guidelines for Responsible Fisheries. FAO, Rome. ISBN 92-5-103962-3
- Cochrane, Kevern L.; Garcia, Serge M. (22 June 2009). A Fishery Manager's Guidebook. John Wiley & Sons. pp. 91–. ISBN 978-1-4051-7085-7.
- Erdogan, Naciye; Duzgunes, Ertug (1 January 2008). "Fisheries Management in the Black Sea Countries". Turkish Journal of Fisheries and Aquatic Sciences. 8 (1): 181–192.
- Beamish, Richard J.; Rothschild, Brian J., eds. (2009). The Future of Fisheries Science in North America. Springer. ISBN 978-1-4020-9210-7.
- "FAO Fisheries & Aquaculture - Code of Conduct for Responsible Fisheries". www.fao.org.
- Pitcher, Kalikoski & Pramod 2006
- Sustainable Fishery system, Charles, A. (ed) (2001). Oxford: Blackwell science. p. 95.
- Costello, Christopher; Gaines, Steven D.; Lynham, John (2008). "Can Catch Shares Prevent Fisheries Collapse?".
- Debora MacKenzie New Scientist: Guaranteed fish quotas halt commercial free-for-all
- A Rising Tide: Scientists find proof that privatising fishing stocks can avert a disaster The Economist, 18 Sept, 2008.
- New study offers solution to global fisheries collapse Eureka alert.
- Soliman, Adam (2014) "Using individual transferable quotas (ITQs) to achieve social policy objectives: A proposed intervention", Marine Policy, 45C: 76–81.
- Soliman, Adam (January 2014). "Individual transferable quotas in world fisheries: Addressing legal and rights-based issues". Ocean & Coastal Management. 87: 102–113. doi:10.1016/j.ocecoaman.2013.09.012.
- AAAS (2005) New Science Sheds Light on Rebuilding Fisheries Archived 17 December 2008 at the Wayback Machine
- FAO (2002) A Fishery Manager's Guidebook - Management Measures and Their Application. Rome. ISBN 92-5-104773-1.
- Shertzer, Kyle W.; Prager, Michael H. (January 2007). "Delay in fishery management: diminished yield, longer rebuilding, and increased probability of stock collapse1". ICES Journal of Marine Science. 64 (1): 149–159. doi:10.1093/icesjms/fsl005.
- Thorpe, Robert B.; Jennings, Simon; Dolder, Paul J.; Zhou, Shijie (September 2017). "Risks and benefits of catching pretty good yield in multispecies mixed fisheries". ICES Journal of Marine Science. 74 (8): 2097–2106. doi:10.1093/icesjms/fsx062.
- Mahon & McConney 2004
- Hilborn, R (2007). "Managing fisheries is managing people: what has been learned?". Fish and Fisheries. 8 (4): 285–296. doi:10.1111/j.1467-2979.2007.00263_2.x.
- Elder 2006
- Jentoft, Svein (January 2004). "Fisheries co-management as empowerment". Marine Policy. 29: 1–7. doi:10.1016/j.marpol.2004.01.003.
- Svein, Jentoft (January 2004). "Fisheries co-management as empowerment". Marine Policy. 29: 1–7. doi:10.1016/j.marpol.2004.01.003.
- Tacconi, Luca; Williams, David Aled (2020). "Corruption and Anti-Corruption in Environmental and Resource Management". Annual Review of Environment and Resources. 45: 305–329. doi:10.1146/annurev-environ-012320-083949.
- "Adkison advocates increased fisheries data gathering". University of Alaska Fairbanks. 2007. Archived from the original on 11 July 2007. Retrieved 14 November 2008.
- "FAO Fisheries Department - FISHERY STATISTICS: RELIABILITY AND POLICY IMPLICATIONS". www.fao.org.
- Gucinski, Lackey, and Spence (1990)
- Hlohowskyj, Brody, and Lackey, (1996)
- Jacobs, A.; Doran, C.; Murray, D. S.; Duffill Telsnig, J.; Laskowski, K. L.; Jones, N. A. R.; Auer, S. K.; Praebel, K. (March 2018). "On the challenges and opportunities facing fish biology: a discussion of five key knowledge gaps" (PDF). Journal of Fish Biology. 92 (3): 690–698. doi:10.1111/jfb.13545. PMID 29537088.
- Wilderbuer, Thomas K; Zhang, Chang Ik (June 1999). "Evaluation of the population dynamics and yield characteristics of Alaska plaice, Pleuronectes quadrituberculatus, in the eastern Bering Sea". Fisheries Research. 41 (2): 183–200. doi:10.1016/S0165-7836(99)00012-0.
- Zabel, Richard W.; Harvey, Chris J.; Katz, Stephen L.; Good, Thomas P.; Levin, Phillip S. (2003). "Ecologically Sustainable Yield: Marine conservation requires a new ecosystem-based concept for fisheries management that looks beyond sustainable yield for individual fish species". American Scientist. 91 (2): 150–157. doi:10.1511/2003.2.150. JSTOR 27858183.
- Caswell, H. 2001. Matrix population models: Construction, analysis and interpretation, 2nd Edition. Sinauer Associates, Sunderland, Massachusetts. ISBN 0-87893-096-5.
- Larkin, PA (1977). "An epitaph for the concept of maximum sustained yield". Transactions of the American Fisheries Society. 106: 1–11. doi:10.1577/1548-8659(1977)106<1:AEFTCO>2.0.CO;2.[permanent dead link]
- Walters, C; Maguire, J (1996). "Lessons for stock assessment from the northern cod collapse". Reviews in Fish Biology and Fisheries. 6 (2): 125–137. doi:10.1007/bf00182340.
- Pitcher TJ and Pauly D (1998) "Rebuilding ecosystems, not sustainability, as the proper goal of fishery management" Archived 13 May 2013 at the Wayback Machine Pages 311-325 in T Pitcher, D Pauly and P Hart, Reinventing Fisheries Management, Chapman & Hall.
- University of Liverpool (2006). "Marine Ecologists To Help Rebuild Decreasing Fish Stocks" ScienceDaily.
- FAO: Fisheries governance: The ecosystem approach to fisheries management Rome. Updated 27 May 2005. Accessed 27 November 2009.
- Francis RC, Hixon MA, Clarke ME, Murawski SA, and Ralston S (2007) Ten commandments for ecosystem-based fisheries scientists Archived 15 January 2009 at the Wayback Machine Proceedings of Coastal Zone 07, Portland, Oregon. Download Archived 17 December 2008 at the Wayback Machine
- Arnason, Kelleher & Willmann 2008
- Looting the Seas Archived 4 March 2012 at the Wayback Machine iWatch News, 17 March 2012.
- Elements of Ecology - Thomas M. Smith, Robert Leo Smith
- Meredith P (2009) Te hī ika – Māori fishing - Traditional practices Te Ara - the Encyclopedia of New Zealand. Updated 2 March 2009. Retrieved 22 February 2011.
- Christy FT (1983) Territorial Use Rights in Fisheries: Definitions and Conditions FAO Fisheries, Technical Paper No. 227, Rome. ISBN 978-92-5-101269-7.
- Hannesson R, Salvanes JG and Squires A (2008) "Technological change and the Tragedy of the Commons: The Lofoten Fishery over Hundred and Thirty Years" Archived 24 July 2011 at the Wayback Machine Institutt for Samfunnsøkonomi. Discussion paper SAM 5 2008.
- Beverton & Holt 1957
- Benson, Norman G. (1971). A Century of Fisheries in North America 1st Edition. Bethesda, MD: American Fisheries Society. ISBN 978-0913235058.
- Hubert, Wayne A. (2010). Inland Fisheries Management in North America. Bethesda, MD: American Fisheries Society. ISBN 978-1-934874-16-5.
- Knudsen, E. Eric (2004). Sustainable Management of North American Fisheries. Bethesda, MD: American Fisheries Society. ISBN 1888569654.
- Beverton 1992
- "Prince Charles calls for greater sustainability in fisheries". London Mercury. Archived from the original on 14 July 2014. Retrieved 13 July 2014.
- Arnason, R; Kelleher, K; Willmann, R (2008). The Sunken Billions: The Economic Justification for Fisheries Reform. World Bank and FAO. ISBN 978-0-8213-7790-1. Archived from the original on 4 May 2010. Retrieved 3 April 2009.
- Beverton, R. J. H.; Holt, S. J. (1957). On the Dynamics of Exploited Fish Populations. Fishery Investigations Series II Volume XIX. Chapman and Hall (Blackburn Press, 2004). ISBN 978-1-930665-94-1.
- Beverton, R. J. H. (1992). Voigtlander, C.W (ed.). Session 4: The state of fisheries science. The State of the World's Fisheries Resources: Proceedings of the World Fisheries Congress, Plenary Sessions. Athens. Archived from the original on 18 December 2007.
- Caddy JF and Mahon R (1995) "Reference points for fisheries management" FAO Fisheries technical paper 347, Rome. ISBN 92-5-103733-7
- Duffy, J. Emmett (2008) Marine biodiversity and food security Encyclopedia of Earth. Updated 25 July 2008.
- Elder, D. (2006). "The Impact of Federal Fishing Policies on Coastal Maine and the Town of Harpswell Thesis". Dept. of Geography [ww.ccsu.edu Central Connecticut University]. Cite journal requires
- Ferguson-Cradler, Gregory. "Fisheries’ collapse and the making of a global event, 1950s–1970s." Journal of Global History 13.3 (2018): 399-424. online
- Froese, R and K Kesner-Reyes (2002)Impact of Fishing on the Abundance of Marine Species International Council for the Exploration of the Sea, ICES CM 2002/L:12.
- Gucinski, Hermann; Lackey, Robert T.; Spence, Brian C. (November 1990). "Global Climate Change: Policy Implications for Fisheries". Fisheries. 15 (6): 33–38. doi:10.1577/1548-8446(1990)015<0033:GCCPIF>2.0.CO;2.
- Hilborn, RAY (February 2012). "The evolution of quantitative marine fisheries management 1985–2010". Natural Resource Modeling. 25 (1): 122–144. doi:10.1111/j.1939-7445.2011.00100.x.
- Hlohowskyj, I; Brody, MS; Lackey, RT (1996). "Methods for assessing the vulnerability of African fisheries resources to climate change". Climate Research. 6: 97–106. Bibcode:1996ClRes...6...97H. doi:10.3354/cr006097.
- Mahon, R.; McConney, P. (2004). "Managing the managers: improving the structure and operation of small fisheries departments, especially in SIDS". Ocean and Coastal Management. 47 (9–10): 529–535. doi:10.1016/j.ocecoaman.2004.09.001.
- Lackey, Robert T. 2005. Fisheries: history, science, and management. pp. 121–129. In: Water Encyclopedia: Surface and Agricultural Water, Jay H. Lehr and Jack Keeley, editors, John Wiley and Sons, Inc., Publishers, New York, 781 pp.
- McGoodwin JR (2001) Understanding the cultures of fishing communities. A key to fisheries management and food security FAO Fisheries, Technical Paper 401. ISBN 978-92-5-104606-7.
- Morgan, Gary; Staples, Derek and Funge-Smith, Simon (2007) Fishing capacity management and illegal, unreported and unregulated fishing in Asia FAO RAP Publication. 2007/17. ISBN 978-92-5-005669-2
- Pitcher T, D Pauly and P Hart (1999) Reinventing Fisheries Management, Kluwer Academic Publishers. ISBN 978-0-7923-5777-3
- Pitcher, TJ; Kalikoski, D; Pramod, G (2006). "Evaluations of Compliance with the FAO (UN) Code of Conduct for Responsible Fisheries UBC Fisheries Centre Research Reports". 14 (2). Fisheries Centre. University of British Columbia. doi:10.14288/1.0058147. Cite journal requires
- Townsend, R; Shotton, Ross and Uchida, H (2008) Case studies in fisheries self-governance FAO Fisheries Technical Paper. No 504. ISBN 978-92-5-105897-8
- Voigtlander, C. W. (Ed.) 1994. The State of the World's Fisheries Resources. Proceedings of the World Fisheries Congress (Athens, 1992), Plenary Sessions. (Oxford & IBH Publishing Co. Pvt. Ltd., 66 Janpath, N.Delhi 110 001, INDIA). 204 p.
- Walters, Carl J.; Martell, Steven J. D. (2004). Fisheries Ecology and Management. Princeton University Press. ISBN 978-0-691-11545-0.<
- UNEP (2007). Procedure for Establishing a Regional System of Fisheries Refugia in the South China Sea and Gulf of Thailand in the context of the UNEP/GEF project entitled: “Reversing Environmental Degradation Trends in the South China Sea and Gulf of Thailand”. South China Sea Knowledge Document No. 4. UNEP/GEF/SCS/Inf.4
- Evolution of Views of Fishery Management In: Sustaining Marine Fisheries (1999) Commission on Geosciences, Environment and Resources: Ocean Studies Board.
- FAO Code of Conduct for Responsible Fisheries
- FAO: Index of Fisheries and Aquaculture Technical Papers Rome.
Lua error in Module:Authority_control at line 1174: attempt to index field 'wikibase' (a nil value).