World Library  
Flag as Inappropriate
Email this Article

Magnuson-Stevens Fisheries Conservation and Management Act of 1976

Article Id: WHEBN0014588305
Reproduction Date:

Title: Magnuson-Stevens Fisheries Conservation and Management Act of 1976  
Author: World Heritage Encyclopedia
Language: English
Subject: USCGC Taney (WHEC-37), Exclusive economic zone, USCGC Munro (WHEC-724), Missions of the United States Coast Guard, Fishing industry in the United States
Collection:
Publisher: World Heritage Encyclopedia
Publication
Date:
 

Magnuson-Stevens Fisheries Conservation and Management Act of 1976


The Magnuson–Stevens Fishery Conservation and Management Act (MFCMA),[1] commonly referred to as the Magnuson–Stevens Act, is the primary law governing marine fisheries management in the United States. The law is named after Warren G. Magnuson, former U.S. senator from Washington state, and Ted Stevens, the former senator from Alaska.

The Magnuson–Stevens Act was originally enacted as the Fishery Conservation and Management Act of 1976.[2] The act has been amended many times over the years. Two major recent sets of amendments to the law were the Sustainable Fisheries Act of 1996[3] and then 10 years later the Magnuson–Stevens Fishery Conservation and Management Reauthorization Act of 2006.[4]

Purpose

The MFCMA was enacted to promote the U.S. fishing industry's optimal exploitation of coastal fisheries by “consolidating control over territorial waters” and establishing eight regional councils to manage fish stocks.[5] The act has been amended several times in response to continued overfishing of major stocks. The most recent version, authorized in 2007, includes seven purposes:[6]

  1. Acting to conserve fishery resources
  2. Supporting enforcement of international fishing agreements
  3. Promoting fishing in line with conservation principles
  4. Providing for the implementation of fishery management plans (FMPs) which achieve optimal yield
  5. Establishing Regional Fishery Management Councils to steward fishery resources through the preparation, monitoring, and revising of plans which (A) enable stake holders to participate in the administration of fisheries and (B) consider social and economic needs of states.
  6. Developing underutilized fisheries
  7. Protecting essential fish habitats

Additionally, the law calls for reducing bycatch and establishing fishery information monitoring systems.[7]

Regulatory mechanisms

Regional Fishery Management Councils are charged with developing and implementing fishery management plans, both to restore depleted stocks and manage healthy stocks.[8] The National Marine Fisheries Service (NMFS) aides the Secretary of Commerce, who evaluates and approves the council’s FMPs. Regional Fishery Management Council members are nominated by the governors of their respective states, and approved by the Secretary of Commerce.

A FMP must specify the criteria which determine when a stock is overfished and the measures needed to rebuild it.[9] Regional councils regulate fishers with mechanisms, including annual catch limits, individual catch limits, community development quotas, and others. The Marine Fish Conservation Network highlighted the most significant changes in the mechanisms utilized in a 2010 report:

“To achieve the goal of ending overfishing … Congress strengthened the role of science in the fishery management process and required fishery managers to establish science based annual catch limits (ACLs) and accountability measures (AMs) for all US fisheries with a deadline of 2010 for all stocks subject to overfishing… The new fisheries law requires the councils’ science advisors, the scientific and statistical committees to make recommendations for ‘acceptable biological catch’ (ABC) which managers may not exceed…”[10]

The ACL is the centerpiece of the report which is supplemented by other mechanisms regulating the types of gear used, licensing vessels, and using of observers on fishing boats. In section 303 b, the Act enumerates the types of actions authorized for use by councils to achieve optimal catch goals. Including

  1. Permitting vessels or operators
  2. Designating Zones and periods where fishing is limited
  3. Limiting sale, catch or transport of certain fish.
  4. Regulating types of fishing equipment
  5. Requiring observers onboard vessels

Regional management councils have taken the controversial step of buying fishing vessels to remove them from the water to reduce the size of the fishing fleet.[11]

Regulatory effectiveness

The act’s results vary for different regions and different fish stocks. It did not prevent the overfishing of many species throughout its first 20 years of existence. This prompted major amendments in 1996 and 2006. The National Marine Fisheries Service issued a report to Congress in 2010 on the status of U.S. fisheries. It reported that of the 192 stocks monitored for overfishing 38 stocks (20%) still have fish “mortality rates that exceed the overfishing threshold … and 42 stocks (22%) are overfished”.[12] This is down from 38% and 48% respectively in 2000.[13] A 2003 NMFS report reviewed achievements of the act since 1996. Highlighting the inconsistent effects of the legislation, it revealed that overfishing was eliminated in 15 major fish stocks while overfishing was initiated in 12 major fish stocks.[14] To improve their overfishing prevention programs, the NMFS has implemented the Fish Stock Sustainability Index (FSSI), which measures key stocks according to their overfishing status and biomass levels. Since the FSSI began the index has increased every year.[15]

The act also has impacts on financial matters. While taxpayers have paid over US$3 billion on NFMS programs since the bills inception,[16] ultimately the fishing industry is most affected by the act’s design flaws and incomplete implementation. According to Zeke Grader, Jr., the executive director of the Pacific Coast Federation of Fishermen's Associations, the largest active trade association of commercial fishermen on the west coast, "Most of the U.S. fisheries stocks are facing a disaster due to over capitalization of the fishing industry and the mismanagement practices of U.S. Department of Commerce's National Marine Fisheries Service (NMFS) and their appointed regional fishery management councils”.[17] Chris Kellogg, chief technical officer for the New England Fishery Management Council emphasizes the tenuous position of many fishers, "On average, my guess is the fishing harvesting industry here in New England is basically covering costs and just on the border of solvency and insolvency".[18]

Stakeholders

Many interest groups are concerned with the forming of fisheries conservation legislation. Fishers, corporations, activist groups and the public all share interest in protecting fishing eco-systems and economies via the MSFCMA.

Fishers advocate measures that encourage regulatory processes to be scaled to the local level and which ensure fishing privileges aren’t concentrated into small groups.[19] They are also aware that if too much competition for finite resources prevails, their livelihood will suffer. Despite this, some fishermen prefer minimal government intervention in their market, defiantly demanding “the right to go broke”.[20]

The fishing industry is a $4billion a year industry.[21] Fish harvesting and processing corporations are invested in the political process to maximize their profits, to protect against foreign competition and to prevent regulations from making their proprietary information available to the public. University, argues that federal legislators cannot forge these relationships largely because they haven’t properly identified what a “fishing community” is. She highlights the successes of the Community Development Quota system employed in some Alaska fisheries.[22]

Non-Governmental Organizations (NGOs) focusing on fish conservation and environmentalism were key forces behind the incremental improvements in the law’s regulatory mechanisms. The Pew Oceans Commission and the US commission on Oceans Policy prompted many of the amendments found within the 2006 reauthorization.[23] Many advocacy groups speak through coalitions. The Marine Fish Conservation Network, for example, represents over 90 member organizations from across the United States.

The public is represented as a stake holder by elected representatives, who ostensibly take them into consideration when drafting ways to protect public resources such as fish stocks.

Critiques

The major criticisms of the act have been its failure to stem overfishing, minimize bycatch, and to hold accountable regional councils that don’t enforce or implement fisheries management plans. Additionally, the act is accused of coddling fishers who make poor business decisions, inadequately protecting ecosystems, and lacking transparency requirements for fishery related data.[24]

Poor enforcement of previous versions of the act is often blamed for depleting stocks. Fishermen have accused each other of cheating on landings and chastised regulators for concentrating the quota allocations into too few hands.[25] Other critics claim the regulatory framework is too “top-down” and alienates local fishers, thereby reducing the likelihood to achieve the cooperation needed to enforce many provisions. Candice May, of Colorado State University, argues that federal legislators can’t forge these relationships largely because they haven’t properly identified what a “fishing community” is. She highlights the successes of the Community Development Quota system employed in some Alaska fisheries.[26]


In response to these types of criticisms, “On May 1, 2010, the National Marine Fisheries Service (NMFS) implemented a new management system for ground fish in New England. It established 17 fishermen-run collectives, called sectors. Sectors were pioneered by fishermen as voluntary, cooperative and community-based, and were designed to protect fleet diversity and coastal communities. The new management system operates on three simple premises:

  • It implements science-based catch limits to rebuild fish populations and prevent overfishing.
  • It incorporates monitoring so fishermen and regulators know exactly how much fish is being caught, and as a result, fishing stops once catch limits have been reached.
  • Each sector receives its own share of the annual catch. While respecting catch limits, the co-ops provide fishermen with the flexibility to set their own fishing guidelines so they can run their businesses more efficiently and profitably. Those who develop more innovative fishing gear can target more of the healthy fish populations and avoid those populations that are struggling.”[27]

As reported at the Council meeting, the first three months of sector operations resulted in (May 1 – August 15):

  • Fishermen earning more money for less fishing under the new system. In 2010, landings are down compared to 2009. Only 85.8 percent of total landings last year were landed this year (for the same period of time). Meanwhile, revenues are up 112.4 percent.
  • Sector fishermen are avoiding weak stocks and targeting robust stocks. The ratio of Georges Bank cod to Georges Bank haddock (in metric tons) in 2009 was 1121:1532. In 2010, it was 743:2768.
  • Landings of Gulf of Maine winter flounder, a stock at very low abundance, are being effectively avoided under sectors. In 2009, 66 metric tons were landed. In 2010, 32 metric tons were landed.”[28]

See also

References

External links

  • PDF version of the Magnuson-Stevens Fishery Conservation and Management Act, as amended through January 12, 2007
  • NOAA National Marine Fisheries Service website on the most recent reauthorization of the Magnusion-Stevens Act
  • NOAA National Marine Fisheries Service website on the Sustainable Fisheries Act of 1996
  • Short overview of the Act by the U.S. Fish and Wildlife Service
  • Pew Environment Group: Rebuilding America's Fisheries with One Single Act
Help improve this article
Sourced from World Heritage Encyclopedia™ licensed under CC BY-SA 3.0
Help to improve this article, make contributions at the Citational Source
This article was sourced from Creative Commons Attribution-ShareAlike License; additional terms may apply. World Heritage Encyclopedia content is assembled from numerous content providers, Open Access Publishing, and in compliance with The Fair Access to Science and Technology Research Act (FASTR), Wikimedia Foundation, Inc., Public Library of Science, The Encyclopedia of Life, Open Book Publishers (OBP), PubMed, U.S. National Library of Medicine, National Center for Biotechnology Information, U.S. National Library of Medicine, National Institutes of Health (NIH), U.S. Department of Health & Human Services, and USA.gov, which sources content from all federal, state, local, tribal, and territorial government publication portals (.gov, .mil, .edu). Funding for USA.gov and content contributors is made possible from the U.S. Congress, E-Government Act of 2002.
 
Crowd sourced content that is contributed to World Heritage Encyclopedia is peer reviewed and edited by our editorial staff to ensure quality scholarly research articles.
 
By using this site, you agree to the Terms of Use and Privacy Policy. World Heritage Encyclopedia™ is a registered trademark of the World Public Library Association, a non-profit organization.
 


Copyright © World Library Foundation. All rights reserved. eBooks from Project Gutenberg are sponsored by the World Library Foundation,
a 501c(4) Member's Support Non-Profit Organization, and is NOT affiliated with any governmental agency or department.