Relevant bibliographies by topics / Fisheries economics

Academic literature on the topic 'Fisheries economics'

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Published: 4 June 2021
Last updated: 6 September 2023

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Journal articles on the topic "Fisheries economics"

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Squires, Dale. "Advances in Fisheries Economics." Fish and Fisheries 11, no. 1 (March 2010): 112–14. http://dx.doi.org/10.1111/j.1467-2979.2009.00348.x.

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Masters, C. "Economics of fisheries development." Long Range Planning 18, no. 1 (February 1985): 118–19. http://dx.doi.org/10.1016/0024-6301(85)90189-x.

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Lawson, Rowena. "Fisheries economics: An introduction." Marine Policy 9, no. 4 (October 1985): 345–46. http://dx.doi.org/10.1016/0308-597x(85)90050-8.

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Appleyard, Philip. "Economics of fisheries development." Marine Policy 9, no. 1 (January 1985): 82. http://dx.doi.org/10.1016/0308-597x(85)90087-9.

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Glassner, M. I. "Economics of fisheries development." Ocean Management 10, no. 1 (September 1986): 75–76. http://dx.doi.org/10.1016/0302-184x(86)90013-2.

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Putri, Hanifa Miranda I. H., I. Wayan Arthana, Elok Faiqoh, Ranny R. Yuneni, and Yuniarti K. Pumpun. "Karakteristik Sosial Ekonomi Nelayan Pemanfaat Hiu Tikus (Alopiidae) di Manggis, Karangasem, Bali." Journal of Marine and Aquatic Sciences 8, no. 2 (February 1, 2023): 297. http://dx.doi.org/10.24843/jmas.2022.v08.i02.p14.

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Thresher sharks are known to have substantial economic value. They are caught globally as target and as bycatch in tuna fisheries. Due to their declining population, they are listed as an appendix II species on CITES, therefore any form of trade and fisheries related to the species have been nationally and internationally regulated. However, information on thresher shark fisheries in Bali is still limited. This study aims to socio-economically characterize thresher shark fishermen in Manggis, Karangasem. The research was conducted in August 2020 – October 2020 by interviewing 53 out of 119 recorded shark fishermen using a structured questionnaire. Shark fishermen use surface longlines to catch thresher sharks (Alopiidae) in between 3 areas, North Nusa Penida-Karangasem, east Nusa Penida and Bangko-Bangko. The fishermen catch sharks exclusively during the months of June-October and catch tuna the rest of the year. Operational costs for 1 boat ranges between Rp 121.000 – Rp 250.000 during 1 round trip. The income generated from shark fishing each trip averages to about Rp 627.714 per boat. Prior to the Covid-19 pandemic, some of the fishermen work jobs in the tourism sector. However, due to the pandemic’s impact on tourism, they have no choice but to be fishermen full time. Although thresher shark fisheries in Manggis are generally small scale, conservation and management strategies need to be implemented to ensure sustainable use of shark resources.
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Sakuma, Yoshiaki. "Fisheries Economics in Mie Prefecture." NIPPON SUISAN GAKKAISHI 61, no. 2 (1995): 251–52. http://dx.doi.org/10.2331/suisan.61.251.

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Mitchell, C. L. "The economics of fisheries management." Fisheries Research 5, no. 4 (August 1987): 414–16. http://dx.doi.org/10.1016/0165-7836(87)90057-9.

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Haynie, Alan C., and Lisa Pfeiffer. "Why economics matters for understanding the effects of climate change on fisheries." ICES Journal of Marine Science 69, no. 7 (February 27, 2012): 1160–67. http://dx.doi.org/10.1093/icesjms/fss021.

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Abstract Haynie, A. C., and Pfeiffer, L. 2012. Why economics matters for understanding the effects of climate change on fisheries. – ICES Journal of Marine Science, 69: . Research attempting to predict the effect of climate change on fisheries often neglects to consider how harvesters respond to changing economic, institutional, and environmental conditions, which leads to the overly simplistic prediction of “fisheries follow fish”. However, climate effects on fisheries can be complex because they arise through physical, biological, and economic mechanisms that interact or may not be well understood. Although most researchers find it obvious to include physical and biological factors in predicting the effects of climate change on fisheries, the behaviour of fish harvesters also matters for these predictions. A general but succinct conceptual framework for investigating the effects of climate change on fisheries that incorporates the biological and economic factors that determine how fisheries operate is presented. The use of this framework will result in more complete, reliable, and relevant investigations of the effects of climate change on fisheries. The uncertainty surrounding long-term projections, however, is inherent in the complexity of the system.
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Frost, Hans, and Peder Andersen. "The Common Fisheries Policy of the European Union and fisheries economics." Marine Policy 30, no. 6 (November 2006): 737–46. http://dx.doi.org/10.1016/j.marpol.2006.01.001.

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Dissertations / Theses on the topic "Fisheries economics"

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Cahill, Paul C. "The economics of fisheries and fisheries management : a partial review." Thesis, McGill University, 1985. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=63301.

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Pascoe, Sean David. "A bioeconomic analysis of the UK fisheries of the English Channel." Thesis, University of Portsmouth, 1998. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.264457.

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The purpose in this thesis was to undertake a bioeconomic analysis of the fisheries of the English Channel. An economic survey of the fishery was undertaken to establish the economic and financial performance of the various fleet segments in the fishery in 1994-95. It was found that the fishery as a whole was producing negligible levels of resource rent, although some boat owners were receiving intra-marginal rents. Long run equilibrium models of sole and plaice were developed and the optimal (profit maximising) level of effort (in beam trawl hours equivalent) was estimated. It was found that the optimal level of effort was substantially lower than the current level of effort expended on these two species. A method for estimating surplus production models which incorporate decreasing returns to effort was also developed and applied to the fishery. A linear programming (LP) model was also developed which incorporate the multi-species and multi-gear features of the fishery. The model was used to estimate the maximum level of profits that could be achieved in the fishery given existing stock conditions. It was found that profits could be increased substantially, but at the cost of a large reduction in fishing employment. A compromise `optimal' was estimate using multi-objective (goal programming) techniques. The LP model was also used to estimate the effects of a restriction on days at sea and reduced total allowable catches of sole and plaice. It was estimated that these policies would impose additional costs on various segments of the fishery, particularly the trawl segments to which they are targeted. Benefits, if any, were likely to be negligible as the policies were estimated to result in increased discarding rather than decreased catch. The model results suggest that the long term level of effort may be more effectively reduced through implementing a charge on access to, or use of, the resource.
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Torres, Julio Alejandro Pena. "Economic analysis of marine industrial fisheries." Thesis, Queen Mary, University of London, 1996. http://qmro.qmul.ac.uk/xmlui/handle/123456789/28956.

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This thesis is a collection of essays on the problem of overfishing in multifirm fisheries with a common property fish stock. We focus on the case of marine industrial fisheries, where the costs of preventing free riding tend to preclude cooperative harvesting. We study the overfishing problem by analysing harvesting incentives that stem from variations in (i) technological (cost, production and biological growth) functions, (ii) institutional factors (access schemes, regulatory agencies' instruments and their monitoring and enforcement powers, harvesting competition), and (iii) objective functions (private firms' planning horizons, welfare functions). Chapter 2 discusses conditions under which a fishing collapse can occur and examines the commonly held argument that fishing collapse is a public bad. Chapter 3 studies Chilean fishing regulations over the last five decades. The regulator's persistent inability to enforce annual quotas is analysed. Distributive disputes and triggered lobbying powers are examined. The late 1980s controversies over a new Chilean fishing law are analysed in-depth from this perspective. Chapter 4 explains the main motivations and key assumptions leading us to the oligopoly harvesting models of chapters 5 (static setting) and 6 (dynamic setting). These models focus on a deterministic single fish species and a single sector harvesting fishery composed of profit maximizing and price taking private firms that compete with each other by following non-cooperative harvesting strategies. These models examine the overfishing rankings that result from comparing Cournot-Nash and Stackelberg equilibria. First best and second best welfare benchmarks are considered. The Cournot-Nash setting is intended to illustrate a large number oligopolistic fishery, while the Stackelberg equilibrium is meant to be a first approximation to analyse the implications of harvesting fisheries subject to industrial concentration. Empirical evidence suggesting the presence of industrial concentration in a series of important marine industrial fisheries is described in chapters 3 and 4.
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Dawson, Robert Donald. "Vertical Integration in Commercial Fisheries." Diss., Virginia Tech, 2003. http://hdl.handle.net/10919/28627.

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Vertical integration has received much attention in the last 25 years and there are well-known theories that explain this behavior. However, the one common thread that runs through virtually all of this research is the assumption of private property rights. Very little attention has been paid to how firms behave when the property rights structure under which they operate changes. The commercial fishing industry is a prime example of an industry where property rights have shifted. Due to problems of over-fishing and over-capitalization, economists have championed the conversion of fisheries from common property or open access resources, to private property through the use of quota programs. Research shows that quota management is effective in reducing capitalization in fisheries, yet there are questions about other effects the programs might have. Among these is a concern over increased vertical integration. Some argue that this is leading to a loss of the independent fisherman that is a part of U.S. history, much like family farms. There is also concern that increased vertical integration is in turn leading to decreased competition in these markets; by owning the quota that is required to fish, processors are increasing their power over the market for unprocessed fish. In response to these and other concerns, the United States Congress imposed a moratorium on the implementation of individual transferable quota-style (ITQ) programs in 1996. Speculation aside, however, there is no empirical evidence to confirm or refute that the use of quota management actually leads to increased vertical coordination. Three fisheries are used as case studies to analyze what affects the decision to vertically coordinate in commercial fisheries. The traditional reasons for vertical integration are to lower transaction costs or to foreclose a market. But now a new factor, shifting property rights, is also considered. Results indicate that the individual characteristics of the fishery are more important than the management or property rights regime itself. This gives some direction to designing management programs that meet our desire to reduce over-capitalization and over-fishing, yet avoid increasing vertical coordination, all the while minimizing the loss of resource rent in the fishery.
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Greenville, Jared William. "Marine Protected Areas: A Tool for Fisheries Management." Thesis, The University of Sydney, 2007. http://hdl.handle.net/2123/1893.

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The management of fisheries has progressed over the past century in an attempt to solve the problem of open access. A range of controls, both economic and non-economic in nature, have been used to ration the use of marine resources. Unfortunately, many controls have failed to correct open access problems. Whilst a recent development in fishery control, protected areas defined as an area with a fishery free of extractive pressure, have been put forward as an arrangement which may, in conjunction with other controls, be used to overcome the over-exploitation of marine resources. Marine protected areas have been advocated in areas where other forms of fishery management are impractical or unsuccessful (Sumaila 1998). Arguments for protected area use are based around the heterogeneous nature of fisheries, uncertainties in marine populations and as a hedge strategy to reduce risks of over-exploitation (Conrad 1999a). Through the protection of biodiversity, improving the resilience of the ecosystem, protected areas may mitigate the effects of negative shocks (Ludwig et al. 1993 and Bostford et al. 1997). Further, protected areas have been suggested as a means to manage uncertainty and environmental stochasticity (Grafton and Kompas 2005 and Grafton et al. 2005). The protection of biomass and habitat has the potential to improve fishery returns even when stocks are not overly exploited, with the benefits accruing even from small-sized protected areas (Grafton et al. 2005). The use of marine protected areas as a management tool has resulted from a recognition that it is important to preserve biological habitats as well as stocks. From a societal point of view, the use of protected areas should be evaluated in the context of changes in resource rent and improvements in welfare. As fishery resources are often owned by a common group, usually society, management objectives should be to maximise the return from use of the resources, whether for extractive or non-extractive purposes. Given this decision criterion, protected areas can be evaluated in the sense of opportunity costs and benefits. Protected areas will influence the return from fishery resources through changes in access to fishing grounds, and thus harvest, effort and resource rent. Once a protected area is established, the flow of biomass from the protected area to the remaining fishing ground, may increase biomass, influence the effects of uncertainty and stochasticity, thus effecting mean harvests, effort and resource rent may increase. Changes in resource rent are dependent on other controls. Protected areas are a ‘blunt’ policy instrument, in the sense that they are not an instrument to capture resource rent or change the incentives of fishers. Models of marine protected areas in fisheries vary in complexity, however, a few key elements are necessary in analysing the effects of protected area creation. First, multi-species interactions have the potential to be significant in determining the outcome from a protected area; second, effort expended in the fishery must be dynamic, that is, it must be endogenously determined by the model as fishers will respond to changes in rent brought about through the establishment of a protected area; third, institutional structures that govern the expenditure of effort within a fishery will play an important role in the effectiveness of protected areas in increasing the resource rent of a fishery; and fourth, environmental stochasticity and uncertainty need to be included in the analysis. A stochastic and deterministic model of a predator-prey meta-population fishery was developed to analyse the effects of protected area creation within a fishery. Such a model has not previously been used to analyse protected area creation. The model was analytically solved to find the optimal biomass of each species in an individual patch. This allowed for a comparison of protected areas under a range of management controls ranging from those which led to open access fishing to those which led to an optimal steady-state biomass. The model allowed for linkages between sub-populations based on differing density related flows. Further, due to the linkages between species on both environmental and economic grounds, the effect of protected areas on different groups which target different species could be analysed. The benefits from protected area creation were classified into unique and non-unique benefits. Unique benefits were defined as those which solely flow from the use of a protected area as a tool in fisheries management. Two unique benefits were defined: • Improvements in the resilience of the fishery; and • Reductions in environmental stochasticity. The ability of a protected area to both improve the resilience of the fishery, and smooth fluctuations in environmental stochasticity have been shown to lead to increases in mean resource rent. Thus, protected areas were shown to form part of an optimal fisheries management structure. Generally, the resilience benefits were maximised for small-sized protected areas, whereas the reduced environmental stochasticity benefits were maximised for larger protected areas. The dispersal system between the protected area and the fishing ground affected the unique benefits from protected area creation. Sink-source dispersal increased the unique benefits from protected area creation, as stock movements occurred independently of relative population densities. The independent flow improved the ability of the protected area to hasten the return of the fishery to a steady-state and lessened the variation of harvests in the open fishing grounds. However, in the case where the protected area led to large differences in population densities, and if the area formed a sub-population that was linked to the surrounding fishing ground by density-dependent dispersal, the unique benefits are likely to be greater than under sink-source dispersal. The non-unique benefits were defined as those which could be obtained from other control mechanisms. These benefits were non-unique as they could be achieved from more stringent controls on fisher behaviour. The determinants of the non-unique benefit in terms of dispersal were the same as for the unique benefits. However, the economic conditions of the fishery determined the magnitude of the non-unique benefits. For fisheries with sub-optimal biomass, the unique benefits were greater than those with optimal steady-state biomass. The non-unique benefits identified from protected area creation were: • Changes in biomass towards optimal levels; • Changes in species biomass ratios towards optimal levels; and • Changes in effort towards optimal levels. Protected areas in fisheries may be an optimal policy choice to achieve the non-unique benefits of protected area creation. Protected areas, it has been argued, are a relatively low cost management tool, due to the lower monitoring and enforcement costs. Thus, the use of protected areas offer a solution to the problems of over extraction of fishery resources for lower transaction costs, which may erode the non-unique benefits under different policy instruments. If this is the case, then a protected area larger than is required to maximise the unique benefits of protected area creation could form part of an optimal fisheries management strategy. Whether the protected area is larger or smaller than the size that maximises both the unique and non-unique benefits of protected area creation would depend on the level of transaction costs involved in using alternative policy instruments. Protected areas were found to have distributional effects on the fishery due to changes in the species biomass ratio towards the predator species post protected area creation. The creation of a protected area will have distributional effects on the fishing industry if different fisheries target the different species separately. Fishers targeting predator species are likely to gain from the establishment of a protected area, as now the aggregate level of stocks of this species is greater, leading to both greater unique and non-unique benefits. For fisheries that target prey species, the benefits of protected area creation are lessened. The increased predation within protected area boundaries limited the unique benefits of the protected area. The low cost nature of a protected area will influence the portion of the fishery used for this type of control given an optimal policy programme. If protected areas are relatively low cost in comparison with other controls they should be used relatively more intensely. Further, the use of protected areas may hasten the evolution of fisheries away from open access exploitation towards controls which maximise the value of the fishery. With lower transaction costs, the ability to adopt protected areas over other forms of management is greater, and by doing so, the movement towards optimal exploitation will improve the discounted value of the fishery. The analysis presented in this thesis examined the benefits of protected areas to fisheries. The focus of the study was placed on the benefits to flow to a fishery if a protected area was used as a tool for wild-harvest fisheries management. Marine protected areas also have the potential to generate a range of other benefits, such as recreational values, non-use values, and potential improvements in consumer surplus from fish caught within fisheries that use protected areas. These other benefits would need to be considered when determining whether or not a protected area should be created in a fishery.
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Bwalya, Samuel Mulenga. "The experimental analysis of the political economics of fisheries governance /." View online ; access limited to URI, 2005. http://0-wwwlib.umi.com.helin.uri.edu/dissertations/dlnow/3188837.

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Lam, Vicky Wing Yee. "Global fisheries economics in the face of change in climate." Thesis, University of British Columbia, 2013. http://hdl.handle.net/2429/45587.

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Climate change and changes in biogeochemical conditions of the ocean lead to changes in distribution of marine species and ocean productivity. These changes would affect fisheries, food security, livelihood of fishing communities and eventually the whole economy in different countries. This thesis uses simulation modelling to assess the direct impacts of change in physical and biogeochemical conditions of the ocean on marine fisheries and the socio-economic implications at both global and regional scales. I develop a new global database of fishing cost, and provide an overview of current fishing cost patterns at national, regional, and global scales. The outcomes lay the foundation for the subsequent economic analysis in the thesis, and should also be useful for other future fisheries economic studies. Using these results and other data from the Sea Around Us Project, I estimate the change in landings of over 800 species of fish within the Exclusive Economic Zones (EEZs) under climate change scenarios based on dynamic bioclimate envelope model (DBEM), and an empirical model. About 75% of EEZs are projected to show declines in landings under the Special Report on Emission Scenario (SRES) A2. Most of them are in developing countries, which are socio-economically more vulnerable to climate change. In West Africa, which is one of the most vulnerable regions to climate change, our model projects that there will be a reduction in landings in the 2050s, with some countries experiencing declines of more than 50% under the “business-as-usual” scenario. This substantial decline not only affects the food supply and security in the region, but also has a negative impact on employment opportunities and the downstream economic impact on the whole society. I also analyze how change in climate and ocean acidity under scenarios of anthropogenic CO₂ emission is expected to affect the economics of marine fisheries in the Arctic region. My model only projected a slight decrease in catch potential of marine fish and invertebrates under the impact of ocean acidification in the 2050s. Future studies accounting for the synergistic effects among climate change, ocean acidification and other factors on marine ecosystems are needed.
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Garrod, Brian. "An economic evaluation of fisheries policy in the United Kingdom." Thesis, University of Portsmouth, 1993. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.332795.

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Herrera, Guillermo E. "Spatial structure and informational asymmetry in the economics of multiple stock renewable resources /." Thesis, Connect to this title online; UW restricted, 2001. http://hdl.handle.net/1773/7425.

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Manning, Peter Robert. "Managing Namibia's marine fisheries : optimal resource use and national development objectives." Thesis, London School of Economics and Political Science (University of London), 1998. http://etheses.lse.ac.uk/2639/.

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Prior to independence, Namibia's marine fisheries had suffered over-fishing, typical of open access exploitation of a common pool resource where there is excess demand. The Namibian Government's policy objectives seek optimal sustainable use of Namibia's fisheries resources and a substantial increase for Namibians of benefit from these resources. In assessing the appropriateness of Namibia's fisheries management system for meeting these objectives, state involvement in the management of the resource is considered, the biological and ecological constraints of the resource are examined and the degree to which national management of fisheries is nested in a global system of fisheries governance is defined. Empirical evidence establishes the critical importance of successfully managing these resources through environmental shocks and the importance for the industry of sufficient economic flexibility, often hindered by overcapacity, to cope with those shocks. Even at low, sub-optimal biomass levels, evidence suggests that substantial resource rent accrues to industry as abnormal profit, or finances overcapacity. Government attempts to redistribute benefit from the resource have been only partly successful. These findings establish the importance of state intervention to ensure that capacity is reduced as close as possible to a bio-economic optimal level, thus maximising resource rent. Collection by the state of a larger proportion of available resource rent would make it less possible for abnormal profits to be earned and make rent less available for financing over-capacity. The additional state finance, representing benefit from the resource, could be directed by the state towards more effective usage in the development process. The management of Namibia's marine fisheries will best be achieved by working towards a system of co-management between the state and industry, providing a framework for nested institutions tailored to the conditions of each fishery, in a joint endeavour to generate a socially optimal use of the resource.
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Books on the topic "Fisheries economics"

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Chen, Xinjun, ed. Fisheries Resources Economics. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-33-4328-3.

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G, Anderson Lee, ed. Fisheries economics: Collected essays. Aldershot, Hants, England: Ashgate, 2002.

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Bjrndal, Trond, Daniel V. Gordon, Ragnar Arnason, and U. Rashid Sumaila, eds. Advances in Fisheries Economics. Oxford, UK: Blackwell Publishing Ltd, 2007. http://dx.doi.org/10.1002/9780470751589.

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Biswas, K. P. Economics in commercial fisheries. Delhi: Daya, 2006.

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Eggert, Håkan. Essays on fisheries economics. Göteborg: Nationalekonomiska institutionen Handelshögskolan vid Göteborgs universitet, 2001.

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1962-, Grafton R. Quentin, ed. Economics for fisheries management. Burlington, VT: Ashgate Pub., 2006.

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R, Dunn Michael, and Whitmarsh David, eds. Fisheries economics: An introduction. London: Mansell Pub., 1985.

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U.S. fishery economics and fishing communities. Hauppauge, N.Y: Nova Science Publishers, 2012.

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Koli, P. A. Economics of fisheries in India. Jaipur: Shruti Publications, 2012.

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The economics of fisheries management. Baltimore: Johns Hopkins University Press, 1986.

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Book chapters on the topic "Fisheries economics"

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Chaboud, Christian. "Fisheries Economics." In Value and Economy of Marine Resources, 153–231. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2014. http://dx.doi.org/10.1002/9781119007791.ch3.

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Clark, Colin W. "Fisheries." In The New Palgrave Dictionary of Economics, 4780–82. London: Palgrave Macmillan UK, 2018. http://dx.doi.org/10.1057/978-1-349-95189-5_512.

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Clark, C. W. "Fisheries." In The New Palgrave Dictionary of Economics, 1–3. London: Palgrave Macmillan UK, 1987. http://dx.doi.org/10.1057/978-1-349-95121-5_512-1.

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Clark, Colin W. "Fisheries." In The New Palgrave Dictionary of Economics, 1–3. London: Palgrave Macmillan UK, 2008. http://dx.doi.org/10.1057/978-1-349-95121-5_512-2.

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Mann, R. H. K. "Fisheries and economics." In Pike, 219–41. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-015-8775-4_9.

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Lewis, Lynne, and Tom Tietenberg. "Fisheries policy." In Environmental Economics and Policy, 145–77. 7th edition. | Abingdon, Oxon ; New York, NY : Routledge, 2020. | Tom Tietenberg appears as the first named author on earlier editions.: Routledge, 2019. http://dx.doi.org/10.4324/9780429503849-7.

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Chen, Xinjun. "Fishery Resource Management and Policy Formulation." In Fisheries Resources Economics, 347–421. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-33-4328-3_8.

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Chen, Xinjun, Gang Li, and Qi Ding. "Bioeconomic Model of Fishery Resources Under Ecological and Technological Interdependencies." In Fisheries Resources Economics, 175–214. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-33-4328-3_4.

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Chen, Xinjun, and Gang Li. "Basic Principles of Resource Economics." In Fisheries Resources Economics, 41–112. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-33-4328-3_2.

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Chen, Xinjun. "Theories and Methods of Fishery Resource Accounting." In Fisheries Resources Economics, 283–322. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-33-4328-3_6.

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Conference papers on the topic "Fisheries economics"

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Shirkova, Elena E. "INSTRUMENTAL SUPPORT OF STRATEGIC MANAGEMENT OF MULTISPECIES FISHERIES." In 14th SGEM GeoConference on ECOLOGY, ECONOMICS, EDUCATION AND LEGISLATION. Stef92 Technology, 2014. http://dx.doi.org/10.5593/sgem2014/b53/s21.030.

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Napier, I. R. "Development and management of crab fisheries in Shetland, Scotland." In Crabs in Cold Water Regions: Biology, Management, and Economics. Alaska Sea Grant, University of Alaska Fairbanks, 2002. http://dx.doi.org/10.4027/ccwrbme.2002.50.

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Tracy, D. A., and S. C. Byersdorfer. "Injuries and aerial exposure to crabs during handling in Bering Sea fisheries." In Crabs in Cold Water Regions: Biology, Management, and Economics. Alaska Sea Grant, University of Alaska Fairbanks, 2002. http://dx.doi.org/10.4027/ccwrbme.2002.16.

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Zaklan, S. D. "Review of the family Lithodidae (Crustacea: Anomura: Paguroidea): Distribution, biology, and fisheries." In Crabs in Cold Water Regions: Biology, Management, and Economics. Alaska Sea Grant, University of Alaska Fairbanks, 2002. http://dx.doi.org/10.4027/ccwrbme.2002.53.

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Chakour, S. C. "Sustainable management of artisanal fisheries in developing countries; the need for expert systems: the case of the Pêchakour Expert System (PES)." In ENVIRONMENTAL ECONOMICS 2008. Southampton, UK: WIT Press, 2008. http://dx.doi.org/10.2495/eeia080211.

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Pawlewicz, Katarzyna. "FISHERIES LOCAL ACTION GROUPS AS A DRIVING FORCE FOR THE IMPLEMENTATION OF ENVIRONMENTAL INVESTMENTS IN POLAND." In 14th SGEM GeoConference on ECOLOGY, ECONOMICS, EDUCATION AND LEGISLATION. Stef92 Technology, 2014. http://dx.doi.org/10.5593/sgem2014/b53/s21.023.

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Schwenzfeier, M., H. Moore, R. Burt, and R. Alinsunurin. "Inquiry for application of data collected by observers deployed in the eastern Bering Sea crab fisheries." In Crabs in Cold Water Regions: Biology, Management, and Economics. Alaska Sea Grant, University of Alaska Fairbanks, 2002. http://dx.doi.org/10.4027/ccwrbme.2002.39.

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Setiawan, Gusjoy, and Faisal Santiago. "Collaborative Governance for Sustainable Development in Indonesia's Fisheries and Marine Resources Governance." In Proceedings of the 1st International Conference on Law, Social Science, Economics, and Education, ICLSSEE 2021, March 6th 2021, Jakarta, Indonesia. EAI, 2021. http://dx.doi.org/10.4108/eai.6-3-2021.2306836.

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Alimuddin, M. Christian Mangiwa, and Muallimin. "Fairness in Profit Sharing of Business in Capture Fisheries in Muslim Community at South Sulawesi." In Proceedings of the 3rd International Conference on Accounting, Management and Economics 2018 (ICAME 2018). Paris, France: Atlantis Press, 2019. http://dx.doi.org/10.2991/icame-18.2019.54.

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Gusrizal, Gusrizal, Adji Suradji Muhammad, Rodi Wahyudi, Rado Yendra, and Ady Muzwardi. "Spatial Autocorrelation Analysis of Natuna’s Capture Fisheries Production through Moran’s I and LISA Indices." In Proceedings of the 1st Maritime, Economics, and Business International Conference, MEBIC 2021, 24-25 September 2021, Tanjungpinang City, Riau Islands Province, Indonesia. EAI, 2021. http://dx.doi.org/10.4108/eai.24-9-2021.2314669.

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Reports on the topic "Fisheries economics"

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Ayers, R., G. P. Course, and G. R. Pasco. Scottish Inshore Fisheries Integrated Data System (SIFIDS): work package (2) final report WP2A: development and pilot deployment of a prototypic autonomous fisheries data harvesting system, and WP2B: investigation into the availability and adaptability of novel technological approaches to data collection. Edited by Mark James and Hannah Ladd-Jones. Marine Alliance for Science and Technology for Scotland (MASTS), 2019. http://dx.doi.org/10.15664/10023.23443.

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[Extract from Executive Summary] To enhance sustainability and foster resilience within Scotland’s inshore fishing communities an effective system of collecting and sharing relevant data is required. To support business decisions made by vessel owners as well as informing fisheries managers and those involved in marine planning it will be vital to collect a range of information which will provide a robust understanding of fishing activity, the economic value of the sector and its importance within local communities. The SIFIDS Project was conceived to assist in attaining these goals by working alongside fishers to develop and test technology to automatically collect and collate data on board vessels, thereby reducing the reporting burden on fishers. The project built upon previous research funded through the European Fisheries Fund (EFF) and was designed to deliver a step change in the way that inshore fisheries in Scotland could be managed in cooperation with the industry. The project focussed on inshore fishing vessels around Scotland, where spatio-temporal information on the distribution of vessels and associated fishing effort is data deficient. The whole project was broken down into 12 highly integrated work packages. This is the integrated report for work packages 2A and 2B, entitled’ Development and Pilot Deployment of a Prototypic Autonomous Fisheries Data Harvesting System’ (2A) and ‘Investigation into the Availability and Adaptability of Novel Technological Approaches to Data Collection’ (2B).
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Fox, Clive J., L. Valcic, and Andrea Veszelovszki. Evidence gathering in support of sustainable Scottish inshore fisheries: work package (4) final report: a pilot study to define the footprint and activities of Scottish inshore fisheries by identifying target fisheries, habitats and associated fish stocks. Edited by Mark James and Hannah Ladd-Jones. Marine Alliance for Science and Technology for Scotland (MASTS), 2015. http://dx.doi.org/10.15664/10023.24673.

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[Extract from Executive Summary] This work was conducted under Work package 4 of the European Fisheries Funded program “Evidence Gathering in Support of Sustainable Scottish Inshore Fisheries”. The overall aim of the program was to work in partnership with Marine Scotland Fisheries Policy and with the Scottish Inshore Fisheries Groups to help develop inshore fisheries management. Specifically the program aims were to establish the location of fishing activities within inshore areas; to identify catch composition and associated fishery impacts; to define the environmental footprint and availability of stocks; to develop economic value within local fisheries and; to establish an information resource base to assist the development of inshore fisheries management provisions.
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Billing, Suzannah-Lynn, Shannon Anderson, Andrew Parker, Martin Eichhorn, Lindsay Louise Vare, and Emily Thomson. Scottish Inshore Fisheries Integrated Data System (SIFIDS): work package 4 final report assessment of socio-economic and cultural characteristics of Scottish inshore fisheries. Edited by Mark James and Hannah Ladd-Jones. Marine Alliance for Science and Technology for Scotland (MASTS), 2018. http://dx.doi.org/10.15664/10023.23450.

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[Extract from Executive Summary] The European Maritime and Fisheries Fund (EMFF) has funded the ‘Scottish Inshore Fisheries Integrated Data System’ (SIFIDS) project, which aims to integrate data collection and analysis for the Scottish inshore fishing industry. SIFIDS Work Package 4 was tasked with assessing the socio-economic and cultural characteristics of Scottish Inshore Fisheries. The aim was to develop replicable frameworks for collecting and analysing cultural data in combination with defining and analysing already available socio-economic datasets. An overview of the current available socio-economic data is presented and used to identify the data gaps. Primary socio-economic and cultural research was conducted to fill these gaps in order to capture complex cultural, social and economic relationships in a usable and useful manner. Some of the results from this Work Package will be incorporated into the platform that SIFIDS Work Package 6 is building. All primary research conducted within this work package followed the University of the Highlands and Islands (UHI) Research Ethics Framework and was granted Ethical Approval by the UHI Research Ethics Committee under code ETH895.
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Fluharty, David L. Characterization and assessment of economic systems in the interior Columbia basin: fisheries. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 2000. http://dx.doi.org/10.2737/pnw-gtr-451.

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Campling, Liam. Fisheries Aspects of ACP-EU Interim Economic Partnership Agreements: Trade and Sustainable Development Implications. Geneva, Switzerland: International Centre for Trade and Sustainable Development, 2008. http://dx.doi.org/10.7215/nr_ip_20081013.

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Doherty, Martin. The Importance of Sanitary and Phytosanitary Measures to Fisheries Negotiations in Economic Partnership Agreements. Geneva, Switzerland: International Centre for Trade and Sustainable Development, 2010. http://dx.doi.org/10.7215/nr_ip_20100204.

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Saavedra, José Jorge, and Gerard Alleng. Sustainable Islands: Defining a Sustainable Development Framework Tailored to the Needs of Islands. Inter-American Development Bank, December 2020. http://dx.doi.org/10.18235/0002902.

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Like other Small Island Developing States (SIDS), Caribbean island economies have intrinsic characteristics that make them vulnerable to external shocks. The recent pandemic highlights the structural problems of small island economies. Due to their remote location and small size, islands lack economies of scale and rely on global supply chains, which are currently disrupted. Islands depend either on service-based economic activities like tourism, which are being affected during the current crisis, or on a single commodity, which makes them extremely vulnerable. Islands must rethink their approach to development, adopting one of sustainable development. The Sustainable Islands Platform aims to create a new approach that targets the needs of Caribbean islands and prescribes circular economy-inspired interventions in key areas such as sanitation, waste management, agriculture, fisheries, tourism, energy, transportation, and health. Traditional approaches have not proven successful in solving developing problems on SIDS. Therefore, a new concept that considers islands in a new way should be considered.
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Hambrey, John, Paul Medley, Sue Evans, Crick Carlton, Carole Beaumont, and Tristan Southall. Evidence gathering in support of sustainable Scottish inshore fisheries: work package (6) final report: integrating stock management considerations with market opportunities in the Scottish inshore fisheries sector – a pilot study. Marine Alliance for Science and Technology for Scotland (MASTS), 2015. http://dx.doi.org/10.15664/10023.24677.

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In June 2014, Hambrey Consulting successfully responded to a call for tenders for research to undertake a pilot assessment of the potential economic and associated benefits of establishing minimum market landing size (MMLS) in excess of minimum legal landing size (MLS) for shellfish; and to evaluate if such an intervention could be undertaken at a regional level. The project was originally conceived as including 3 case studies, but the scope of the research led us to focus mainly on the trawl and creel fishery for Nephrops prosecuted by the fleet based in Skye and SW Ross. The basic framework for the assessment approach was to: Develop an economic profile of the case study area and its fishing fleet; Review and synthesise existing data on size profile of the catch, the factors that affect size, including costs associated with individual (vessel) actions or strategies to increase the size profile of the catch; Analyse market and market trends, and the prices for different sizes of product; Develop economic models of representative fishing enterprises, taking account of the relationships between costs and returns and the size profile of the catch; Use plausible scenarios to explore likely short term economic consequences of any changes in MMLS; Use yield and utility per recruit analysis to explore possible yield benefits associated with increased MMLS.
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Naddafi, Rahmat, Göran Sundblad, Alfred Sandström, Lachlan Fetterplace, Jerker Vinterstare, Martin Ogonowski, and Nataliia Kulatska. Developing management goals and associated assessment methods for Sweden’s nationally managed fish stocks : a project synthesis. Department of Aquatic Resources, Swedish University of Agricultural Sciences, 2023. http://dx.doi.org/10.54612/a.31cfjep2i0.

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This report summarizes and synthesizes results from the Swedish Agency of Marine and Water Management (SwAM, or HaV) funded project “Förvaltningsmål för nationella arter (Management goals for nationally managed species)”. The objectives of the project have been to promote the development of management goals and associated status assessment methods and indicators, as well as reference points, for some nationally managed fish stocks both in coastal as well as freshwater areas. The report focusses largely on species and stocks that can be defined as data-poor. Such stocks are characterised by marked limitations in data availability and/or resources allocated to detailed analytical stock projections. Data-poor stocks also often lack carefully formulated management goals and associated methods and indicators for assessing stock status. In this report, we provide an overview of potential assessment methods and indicators and try to synthesise how they work and what the strengths and weaknesses are by applying them to selected data poor stocks such as pikeperch, pike, whitefish, and vendace. We also discuss how they relate to different potential management goals and provide recommendations for their application. We grouped the indicators and assessment methods by the three categories that are now used in the yearly status assessment framework provided by SLU Aqua (Resursöversikten/Fiskbarometern) – i) mortality, ii) abundance/biomass and iii) size/age structure. The results are also described for these three main categories of assessment indicators. Included is also a status report from a size- and age-based population dynamics model (Stock Synthesis 3) that is being developed for pikeperch in Lake Hjälmaren. An important experience from the project is that to improve the assessment methods for Swedish national fish stocks, it is important that managers develop both general as well as more detailed quantitative goals for the individual stocks. This should ideally be conducted in various forms of collaboration with the main stakeholders and scientists involved with assessment as participatory processes foster legitimacy. Carefully articulated management goals, which are possible to translate into quantitative targets, will facilitate the development of various approaches and methods to monitor stock statuses. Given the strong and complex interactions of fish and their environments it is also important to consider other pressures than fisheries when developing indicators and assessment methods. Our synthesis highlights a number of areas where the assessment of data-poor stocks can be improved: 1. Apply precautionary principles for data-limited stocks, particularly ones that are known to be vulnerable to exploitation. 2. Tailor approaches to how fisheries are managed in Sweden. Swedish nationally managed fish stocks are not managed by quotas (with one exception, vendace in the Bothnian Bay) and do not aim for maximum sustainable yield. Instead, the coastal and inland fisheries are managed by regulating the effort in the small-scale commercial fisheries (number of fishers/licenses and amount of gear). Regulation of recreational and subsistence fisheries effort, in terms of licenses or number of fishers) is not applied, nor possible since the fisheries is lacking obligatory notification and reporting systems. All national fisheries, however, are regulated by various technical measures (closed areas, size-limits, bag-limits, gear restrictions etc). Thus, goals and assessment methods that result in harvest limits or quota recommendations expressed in e.g. biomass/numbers are difficult to use as basis for management. Instead, there is a need for alternative management goals and associated assessment methods. 3. Use best practice methods and indicators and adapt as scientific knowledge is developed. Data-limited methods are developing rapidly, and new methods/approaches are proposed in the scientific literature every year. It is thus important to be updated on the most recent developments. 4. Clearly describe limitations/assumptions of methods used. It is important to be aware of and critically evaluate the assumptions underlying the analyses, and to carefully communicate uncertainty together with the stock status assessment. 5. Be particularly careful with low sample numbers. Many indicators and methods can be applied also on small sample sizes, however, the accuracy and precision of the estimates risk being low in such cases. 6. Accept that there is no "gold standard" for fisheries assessment. Each case study is unique and needs to be balanced against data availability, local needs and other important factors. This also means that analysts need to be careful when using generic reference levels or “borrowing” data from other stocks. 7. If possible, use several different methods/indicators. Although several indicators aim to measure similar aspects of the stock, small methodological differences can support the overall interpretation of individual indicator values. It is particularly important to incorporate many aspects and indicators (size/age/abundance/mortality) in order to produce a balanced assessment. 8. Develop means of communication. Indicators and goals should be easy to understand. However, interpretation of results from multi-indicator frameworks can be challenging. There is thus a need for finding ways of communication that can convey complicated results in a simple-to-understand manner. 9. For details on additional improvements, we refer the reader to the sub-header “recommendations for the future” found under each chapter. The implementation of Stock Synthesis for pikeperch in Lake Hjälmaren showed that it is possible to develop a more ambitious and detailed stock assessment model for a relatively data-poor stock. The model results partly support earlier interpretations of the development of the stock and the importance of the changes in regulations in 2001 (increased minimum size, increased mesh size and reduced mortality of undersized pikeperch). Before the model can be implemented and used for practical management, a number of actions for improvement are needed, which are highlighted in the relevant chapter. The most important next step is establishing management goals and reference levels for this stock. We recommend that such a dialogue is initiated by managers. The fisheries management goals should consider both biomass, fisheries mortality and size-based targets. To conclude, we stress the importance of improving all ongoing aspects related to the assessments of data-poor Swedish stocks. Strong local stocks and sustainable fisheries are vital for a variety of fisheries-related businesses and practices, particularly in rural areas, providing economical and societal value. Fishes also have important roles in aquatic food-webs and it is important that ecological values are managed wisely in order to reach targets for water quality, ecosystem structure and diversity. Given the strong and complex interactions of fish and their environments it is also important to consider other pressures than fisheries when developing indicators and assessment methods.
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Tidd, Alexander N., Richard A. Ayers, Grant P. Course, and Guy R. Pasco. Scottish Inshore Fisheries Integrated Data System (SIFIDS): work package 6 final report development of a pilot relational data resource for the collation and interpretation of inshore fisheries data. Edited by Mark James and Hannah Ladd-Jones. Marine Alliance for Science and Technology for Scotland (MASTS), 2019. http://dx.doi.org/10.15664/10023.23452.

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[Extract from Executive Summary] The competition for space from competing sectors in the coastal waters of Scotland has never been greater and thus there is a growing a need for interactive seascape planning tools that encompass all marine activities. Similarly, the need to gather data to inform decision makers, especially in the fishing industry, has become essential to provide advice on the economic impact on fishing fleets both in terms of alternative conservation measures (e.g. effort limitations, temporal and spatial closures) as well as the overlap with other activities, thereby allowing stakeholders to derive a preferred option. The SIFIDS project was conceived to allow the different relevant data sources to be identified and to allow these data to be collated in one place, rather than as isolated data sets with multiple data owners. The online interactive tool developed as part of the project (Work Package 6) brought together relevant data sets and developed data storage facilities and a user interface to allow various types of user to view and interrogate the data. Some of these data sets were obtained as static layers which could sit as background data e.g. substrate type, UK fishing limits; whilst other data came directly from electronic monitoring systems developed as part of the SIFIDS project. The main non-static data source was Work Package 2, which was collecting data from a sample of volunteer inshore fishing vessels (<12m). This included data on location; time; vessel speed; count, time and position of deployment of strings of creels (or as fleets and pots as they are also known respectively); and a count of how many creels were hauled on these strings. The interactive online tool allowed all the above data to be collated in a specially designed database and displayed in near real time on the web-based application.
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