Marine Protected Areas: Economic and Social Implications
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A COMPARATIVE ACCOUNT of the SMALL PELAGIC FISHERIES in the APFIC REGION by M
A COMPARATIVE ACCOUNT OF THE SMALL PELAGIC FISHERIES IN THE APFIC REGION by M. Devaraj and E. Vivekanandan Central Marine Fisheries Research Institute Cocbin-682014, India Abstract The production of the small pe/agics in the APFIC region was 1.2 mt/sq. km during 1995. Among the four areas in the region, the small pe/agics have registered (i) the maximum annual fluctuations in the western Indian Ocean; (ii) the highest increase duri'}i the past two decades along the west coast of Thailand in the eastern Indian Ocean; and (iii) the consistent decline in the landings during the past one decade along the Japanese coast in the northwest Pacific Ocean. The short rnackerels emerged as the largest fishery in the APFlC region, fom'ing 19.5% of the landings of the small pelagics in 1995. The group consisting afthe sardines and the anchovies has shown clear signs of decline during the past one decade in almost the entire region. Most of the small pelagics have unique biological characteristics such as fast growth, short longevity, late maturity, high nalllral mortality, shoaling behaviour, high fecundity and severe recruitment fluctuations. As many species of the small pelagics undertake migration, collaborative research programmes and close coordination are required among the APFle countries for the stock assessment of all the major species. The management measures under implementation in these countries have been reviewed, with suggestions for regional cooperation for the management of the stocks of the small pelagics. INTRODUCTION The Asia-Pacific Fishery Commission covers four oceanic areas, which have been classified by the FAO as the western Indian Ocean (FAO Statistical Area 51), eastern Indian Ocean (Area 57) , northwest Pacific Ocean (Area 61) and western central Pacific Ocean (Area 71). -
Economics and the Resumption of Commercial Whaling
WORKSHOP IN POLITICAL THEORY AND POLICY ANALYSIS 613 NORTH PARK INDIANA UNIVERSITY BLOOMINGTON, IN 47408-3695 U.SLA, Economics and the Resumption of Commercial Whaling by Jon Conrad and Trend BjomdaT The authors are Professors at Cornell University and the Norwegian School of Economics and Business Administration, respectively. Economics and the Resumption of Commercial Whaling ,..,„.. , :vr<; *Yi ABSTRACT " X •"•,'/! .1;>'A7; • There is now strong scientific evidence that several species of baleen whale and possibly the sperm whale, have recovered to levels that would support commercial harvest. The stock of fin whales (Balaenoptera physalus) off the eastern coast of Iceland and the minke whale (Balaenoptera acutorostrata) in the Northeast Atlantic, off the coast of Japan and in the Southern Ocean are prime candidates for commercial harvest. Should commercial whaling be resumed? If so, what role should economics play in determining the level of harvest and management policies? A bioeconomic model for baleen whales is developed and applied to the stock of minke whales in the Northeast Atlantic. A delay- difference equation is used to model the population dynamics and an exponential production function is estimated relating harvest, to population size and the number of catcher vessels. If whaling is resumed, the optimal stock size and harvest may critically depend on the price-cost ratio and catcher productivity. We identify plausible combinations of price, cost and productivity where whaling is not optimal and the minke whale population in the Northeast Atlantic equilibrates at about 82,000 adult animals. Under a high price-cost ratio and high catcher productivity, the optimal stock ranges from 51,000 to 59,000 whales supporting a harvest of 1,600 to 1,750 whales by 90 to 115 catchers. -
Economic Incentives and Overfishing: a Bioeconomic Vulnerability Index
Vol. 530: 223–232, 2015 MARINE ECOLOGY PROGRESS SERIES Published June 18 doi: 10.3354/meps11135 Mar Ecol Prog Ser Contribution to the Theme Section ‘Economics of marine ecosystem conservation’ FREE ACCESS Economic incentives and overfishing: a bioeconomic vulnerability index William W. L. Cheung1,*, U. Rashid Sumaila2 1Changing Oceans Research Unit and 2Fisheries Economics Research Unit, University of British Columbia, 2202 Main Mall, Vancouver, BC V6T 1Z4, Canada ABSTRACT: Bioeconomic theory predicts that the trade-offs between maximization of economic benefits and conservation of vulnerable marine species can be assessed using the ratio between the discount rate of fishers and the intrinsic rate of growth of the exploited populations. In this paper, we use this theory to identify areas of the global ocean where higher vulnerability of fishes to overfishing would be expected in the absence of management. We derive an index to evaluate the level of vulnerability by comparing discount rates and fishes’ intrinsic population growth rates. Using published discount rates of countries that are reported to fish in the ocean and estimating the intrinsic population growth rate for major exploited fishes in the world, we calculate the vulnerability index for each 0.5° latitude × 0.5° longitude grid for each taxon and each fishing country. Our study shows that vulnerability is inherently high on the northeastern coast of Canada, the Pacific coast of Mexico, the Peruvian coast, in the South Pacific, on the southern and southeastern coast of Africa, and in the Antarctic region. It should be noted that this index does not account for the management regime currently in place in different areas, and thus mainly reflects the vulnerability resulting from the intrinsic life history characteristics of the fish species being targeted and the discount rates of the fishers exploiting them. -
Why Study Bycatch? an Introduction to the Theme Section on Fisheries Bycatch
Vol. 5: 91–102, 2008 ENDANGERED SPECIES RESEARCH Printed December 2008 doi: 10.3354/esr00175 Endang Species Res Published online December xx, 2008 Contribution to the Theme Section ‘Fisheries bycatch problems and solutions’ OPENPEN ACCESSCCESS Why study bycatch? An introduction to the Theme Section on fisheries bycatch Candan U. Soykan1,*, Jeffrey E. Moore2, Ramunas ¯ 5ydelis2, Larry B. Crowder2, Carl Safina3, Rebecca L. Lewison1 1Biology Department, San Diego State University, 5500 Campanile Dr., San Diego, California 92182-4614, USA 2Center for Marine Conservation, Nicholas School of the Environment, Duke University Marine Laboratory, 135 Duke Marine Lab Road, Beaufort,North Carolina 28516, USA 3Blue Ocean Institute, PO Box 250, East Norwich, New York 11732, USA ABSTRACT: Several high-profile examples of fisheries bycatch involving marine megafauna (e.g. dolphins in tuna purse-seines, albatrosses in pelagic longlines, sea turtles in shrimp trawls) have drawn attention to the unintentional capture of non-target species during fishing operations, and have resulted in a dramatic increase in bycatch research over the past 2 decades. Although a number of successful mitigation measures have been developed, the scope of the bycatch problem far exceeds our current capacity to deal with it. Specifically, we lack a comprehensive understanding of bycatch rates across species, fisheries, and ocean basins, and, with few exceptions, we lack data on demographic responses to bycatch or the in situ effectiveness of existing mitigation measures. As an introduction to this theme section of Endangered Species Research ‘Fisheries bycatch: problems and solutions’, we focus on 5 bycatch-related questions that require research attention, building on exam- ples from the current literature and the contributions to this Theme Section. -
Ecosystem-Based Fisheries Management Improving the Resilience of Ocean Ecosystems to Support Fish Populations, Coastal Communities
A brief from March 2014 Ecosystem-Based Fisheries Management Improving the resilience of ocean ecosystems to support fish populations, coastal communities The fish on the end of your line, the little forage fish that feed the big fish, the corals that build reef habitats, and the catch of the day in your favorite restaurant are interconnected parts of a vibrant ocean ecosystem. Ensuring the long-term health of important marine species will depend upon our ability to understand and account for the interactions among those species, their environment, and the people who rely upon them for food, commerce, and sport. This comprehensive approach, called ecosystem-based fisheries management, is needed to conserve the healthy ecosystems essential to the sustainability of our fisheries and to deal with the increasingly complex challenges facing our oceans. The United States is a global leader in fisheries management and has made great strides in ending overfishing (the problem of catching fish faster than they can reproduce) and rebuilding vulnerable populations under the Magnuson-Stevens Fishery Conservation and Management Act—the primary law governing U.S. ocean fisheries. In many regions of our nation, this progress has helped reestablish more abundant fish populations and created economic benefits for the fishing industry and coastal communities. Core conservation policies added to the law in 1996 and 2007 are fundamental to improving individual fish populations and returning value to fishermen. We must maintain them as the foundation for sustainable management. But the United States should make the transition from a species-by-species approach to ecosystem-based fisheries management to meet the rising and urgent challenges of damaged ocean environments and dynamic, changing oceans. -
Marine Protected Areas (Mpas) in Management 1 of Coral Reefs
ISRS BRIEFING PAPER 1 MARINE PROTECTED AREAS (MPAS) IN MANAGEMENT 1 OF CORAL REEFS SYNOPSIS Marine protected areas (MPAs) may stop all extractive uses, protect particular species or locally prohibit specific kinds of fishing. These areas may be established for reasons of conservation, tourism or fisheries management. This briefing paper discusses the potential uses of MPAs, factors that have affected their success and the conditions under which they are likely to be effective. ¾ MPAs are often established as a conservation tool, allowing protection of species sensitive to fishing and thus preserving intact ecosystems, their processes and biodiversity and ultimately their resilience to perturbations. ¾ Increases in charismatic species such as large groupers in MPAs combined with the perception that the reefs there are relatively pristine mean that MPAs can play a significant role in tourism. ¾ By reducing fishing mortality, effective MPAs have positive effects locally on abundances, biomass, sizes and reproductive outputs of many exploitable site- attached reef species. ¾ Because high biomass of focal species is sought but this is quickly depleted and is slow to recover, poaching is a problem in most reef MPAs. ¾ Target-species ‘spillover’ into fishing areas is likely occurring close to the MPA boundaries and benefits will often be related to MPA size. Evidence for MPAs acting as a source of larval export remains weak. ¾ The science of MPAs is at an early stage of its development and MPAs will rarely suffice alone to address the main objectives of fisheries management; concomitant control of effort and other measures are needed to reduce fishery impacts, sustain yields or help stocks to recover. -
Study on the Economic Benefits of Marine Protected Areas Literature Review Analysis
Study on the economic benefits of Marine Protected Areas Literature review analysis Written by ICF Consulting Services Limited, in association with IEEP and PML Sept 2017 EUROPEAN COMMISSION Executive Agency for Small and Medium-sized Enterprises (EASME) Unit A.3 — EMFF E-mail: [email protected] European Commission B-1049 Brussels EUROPEAN COMMISSION Study on the economic benefits of Marine Protected Areas Literature review analysis Executive Agency for Small and Medium-sized Enterprises (EASME) Contract No EASME/EMFF/2015/1.3.1.8/SI2.737373 2018 EN Study on the economic benefits of Marine Protected Areas Europe Direct is a service to help you find answers to your questions about the European Union. Freephone number (*): 00 800 6 7 8 9 10 11 (*) The information given is free, as are most calls (though some operators, phone boxes or hotels may charge you). LEGAL NOTICE This document has been prepared for the European Commission however it reflects the views only of the authors, and the Commission cannot be held responsible for any use which may be made of the information contained therein. More information on the European Union is available on the Internet (http://www.europa.eu). Luxembourg: Publications Office of the European Union, 2018 ISBN 978-92-9202-379-9 DOI 10.2826/40733 © European Union, 2018 Study on the economic benefits of Marine Protected Areas Report authors Pantzar, Mia (IEEP) Russi, Daniela (IEEP) Hooper, Tara (PML) Haines, Rupert (ICF) Quality review Rayment, Matt (ICF) Kettunen, Marianne (IEEP) Study on the economic benefits of Marine Protected Areas Table of Contents Executive summary .......................................................................................... -
Economics of Marine Protected Areas As a Tool for Fisheries Management
Economics of Marine Protected Areas as a Tool for Fisheries Management Greenville, J.W. Agricultural and Resource Economics, The University of Sydney, E-mail: [email protected] Keywords: Fisheries Management; Marine Protected Areas; Bioeconomics EXTENDED ABSTRACT greater the benefits from protected area establishment as more of the biomass that occurs The use of marine protected areas as a fishery within the protected area is likely to flow to the management tool has been suggested as a hedge surrounding fishery, offsetting the effects of against management failures and variation in reduced fishing area. The value of small sized harvests. If successful, protected areas have the protected areas is enhanced through the density- potential to increase the level of resource rent dependent flows. Under sink-source flows, derived from the extraction of fishery resources. differences in relative densities do not encourage In this paper, a stochastic bioeconomic model of a increased flows from the protected areas due to multi-species fishery is used to test the differences in patch population density, making the performance of protected areas as a management level of dispersal more dependent on protected area tool in a two patch, two species fishery with size. Given this, when sink-source flows are likely, heterogeneous environments. The differences in a minimum size protected area is required before the environments occur through each patch benefits to the fishery can be obtained. having its own growth rates and internal dynamics. Protected areas are analyzed under The creation of a marine protected area in the density-dependent and sink-source dispersal Manning Bioregion is likely to have different relationships between the environments within the distributional effects on the two fisheries examined fishery. -
Critical Habitats and Biodiversity: Inventory, Thresholds and Governance
Commissioned by BLUE PAPER Summary for Decision-Makers Critical Habitats and Biodiversity: Inventory, Thresholds and Governance Global biodiversity loss results from decades of unsustainable use of the marine environment and rep- resents a major threat to the ecosystem services on which we, and future generations, depend. In the past century, overexploitation of fisheries and the effects of bycatch have caused species to decline whilst coastal reclamation and land-use change—together with pollution and, increasingly, climate change—have led to vast losses of many valuable coastal habitats, estimated at an average of 30–50 percent.1 Despite advances in understanding how marine species and habitats are distributed in the ocean, trends in marine biodiversity are difficult to ascertain. This results from the very patchy state of knowl- edge of marine biodiversity, which leads to biases in understanding different geographic areas, groups of species, habitat distribution and patterns of decline. To address the data gap in our understanding of marine biodiversity and ecosystem integrity, it is crucial to establish the capacity to assess current baselines and trends through survey and monitoring activities. Only increased knowledge and understanding of the above will be able to inform ocean manage- ment and conservation strategies capable of reversing the current loss trend in marine biodiversity. A new paper2 commissioned by the High Level Panel for a Sustainable Ocean Economy increases our understanding of these trends by analysing the links between biodiversity and ecosystem functioning (including tipping points for degradation) and unpacks the link between protection and gross domes- tic product (GDP). In doing so, the paper provides an updated catalogue of marine habitats and biodiversity and outlines five priorities for changing the current trajectory of decline. -
Marine Protected Areas
Marine Protected Areas Read the passage below. How do oceans affect you? If you live far from the coast, you might think they don’t. But life on this planet depends on the oceans. They cover almost three-quarters of the planet and hold 97 percent of the Earth’s water. The phytoplankton that live on the oceans’ surface produce 70 percent of the oxygen in the atmosphere. Oceans are a vital source of food and other resources, and an economic engine for many communities. For all the oceans provide us, we haven’t always been so responsible in our stewardship. “The ocean was thought of as a dumping ground for so long,” says Caitlyn Toropova of the International Union for Conservation of Nature (IUCN). “There was a sense that there was no way we could harm it because it is so vast.” But human activities are having a negative impact on many of the world’s oceans, jeopardizing marine life, habitat, and ecosystems. These threats include overfishing or destructive fishing, coastal development, pollution and runoff, and the introduction of non-native species. Climate change is also having a big effect by causing warming seas and rising acidification. The realization that something needs to be done to stem or reverse the damage has led to the creation of Marine Protected Areas (MPAs). Broadly speaking, marine protected areas are regions of the ocean where human activity is limited. Specifics differ around the globe, but the United States defines a marine protected area as “any area of the marine environment that has been reserved by federal, state, tribal, territorial, or local laws or regulations to provide lasting protection for part or all of the natural and cultural resources therein.” There are approximately 5,000 designated MPAs around the world, and many more that are not officially recognized, says Toropova, the conservation group’s coordination officer for marine protected areas. -
Coastal Upwelling Revisited: Ekman, Bakun, and Improved 10.1029/2018JC014187 Upwelling Indices for the U.S
Journal of Geophysical Research: Oceans RESEARCH ARTICLE Coastal Upwelling Revisited: Ekman, Bakun, and Improved 10.1029/2018JC014187 Upwelling Indices for the U.S. West Coast Key Points: Michael G. Jacox1,2 , Christopher A. Edwards3 , Elliott L. Hazen1 , and Steven J. Bograd1 • New upwelling indices are presented – for the U.S. West Coast (31 47°N) to 1NOAA Southwest Fisheries Science Center, Monterey, CA, USA, 2NOAA Earth System Research Laboratory, Boulder, CO, address shortcomings in historical 3 indices USA, University of California, Santa Cruz, CA, USA • The Coastal Upwelling Transport Index (CUTI) estimates vertical volume transport (i.e., Abstract Coastal upwelling is responsible for thriving marine ecosystems and fisheries that are upwelling/downwelling) disproportionately productive relative to their surface area, particularly in the world’s major eastern • The Biologically Effective Upwelling ’ Transport Index (BEUTI) estimates boundary upwelling systems. Along oceanic eastern boundaries, equatorward wind stress and the Earth s vertical nitrate flux rotation combine to drive a near-surface layer of water offshore, a process called Ekman transport. Similarly, positive wind stress curl drives divergence in the surface Ekman layer and consequently upwelling from Supporting Information: below, a process known as Ekman suction. In both cases, displaced water is replaced by upwelling of relatively • Supporting Information S1 nutrient-rich water from below, which stimulates the growth of microscopic phytoplankton that form the base of the marine food web. Ekman theory is foundational and underlies the calculation of upwelling indices Correspondence to: such as the “Bakun Index” that are ubiquitous in eastern boundary upwelling system studies. While generally M. G. Jacox, fi [email protected] valuable rst-order descriptions, these indices and their underlying theory provide an incomplete picture of coastal upwelling. -
Other Processes Regulating Ecosystem Productivity and Fish Production in the Western Indian Ocean Andrew Bakun, Claude Ray, and Salvador Lluch-Cota
CoaStalUpwellinO' and Other Processes Regulating Ecosystem Productivity and Fish Production in the Western Indian Ocean Andrew Bakun, Claude Ray, and Salvador Lluch-Cota Abstract /1 Theseasonal intensity of wind-induced coastal upwelling in the western Indian Ocean is investigated. The upwelling off Northeast Somalia stands out as the dominant upwelling feature in the region, producing by far the strongest seasonal upwelling pulse that exists as a; regular feature in any ocean on our planet. It is surmised that the productive pelagic fish habitat off Southwest India may owe its particularly favorable attributes to coastal trapped wave propagation originating in a region of very strong wind-driven offshore trans port near the southern extremity of the Indian Subcontinent. Effects of relatively mild austral summer upwelling that occurs in certain coastal ecosystems of the southern hemi sphere may be suppressed by the effects of intense onshore transport impacting these areas during the opposite (SW Monsoon) period. An explanation for the extreme paucity of fish landings, as well as for the unusually high production of oceanic (tuna) fisheries relative to coastal fisheries, is sought in the extremely dissipative nature of the physical systems of the region. In this respect, it appears that the Gulf of Aden and some areas within the Mozambique Channel could act as important retention areas and sources of i "see6stock" for maintenance of the function and dillersitv of the lamer reoional biolooical , !I ecosystems. 103 104 large Marine EcosySlIlms ofthe Indian Ocean - . Introduction The western Indian Ocean is the site ofsome of the most dynamically varying-. large marine ecosystems (LMEs) that exist on our planet.