Three Indicators to Deal with Overfishing
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Recipes for Your Sustainable Seafood
Recipes for your sustainable seafood Not sure how to cook what’s on offer at your local fish merchant? Here we recommend the fish that are sustainable to buy and suggest some recipes to try with them. Brown crab Cancer pagurus Brown crab, also known as edible crab, is the heaviest British crab. About a third of the weight of the crab is meat, two thirds is white and third is brown. It's used to make 'dressed crab' where the shell is cleaned out and used as the dish. Crab is also used to make fish cakes, crab sticks and paste. Brown crabs mature at about 10 years and averagely lives for 30 years, but some have been known to go on till they're 100! The vast majority of brown crabs in the UK are caught by potting. This is a low impact and relatively selective method of fishing, any bycatch or discards can be returned alive to the sea with high survival rates. Brown crab from the Inshore Potting Agreement Area in Devon, the Western Channel or Cornwall are the best choices for crab in the UK. Avoid eating crabs below the minimum landing size (13-14 cm in most areas of the UK) and crab claws, unless it is certain they have been removed from the animal after landing. Egg-bearing or "berried" females should be avoided at all times to allow them to spawn. (Information source: MSC Good Fish Guide) Brown crab Recipes - These four recipes from The Guardian include jungle curry with crab and a spring salad. -
Historical Overfishing and the Recent Collapse of Coastal Ecosystems
E COLOGY T HROUGH T IME REVIEW Historical Overfishing and the Recent Collapse of Coastal Ecosystems Jeremy B. C. Jackson,1,2* Michael X. Kirby,3 Wolfgang H. Berger,1 Karen A. Bjorndal,4 Louis W. Botsford,5 Bruce J. Bourque,6 Roger H. Bradbury,7 Richard Cooke,2 Jon Erlandson,8 James A. Estes,9 Terence P. Hughes,10 Susan Kidwell,11 Carina B. Lange,1 Hunter S. Lenihan,12 John M. Pandolfi,13 Charles H. Peterson,12 Robert S. Steneck,14 Mia J. Tegner,1† Robert R. Warner15 Ecological extinction caused by overfishing precedes all other pervasive longer term cycles or shifts in oceanographic human disturbance to coastal ecosystems, including pollution, degrada- regimes and productivity (15–17). To help ad- tion of water quality, and anthropogenic climate change. Historical abun- dress this problem, we describe ecosystem dances of large consumer species were fantastically large in comparison structure predating modern ecological studies with recent observations. Paleoecological, archaeological, and historical using well-dated time series based on biological data show that time lags of decades to centuries occurred between the (18, 19), biogeochemical (20, 21), physical onset of overfishing and consequent changes in ecological communities, (22), and historical (23) proxies that are infor- because unfished species of similar trophic level assumed the ecological mative over a variety of spatial scales and bio- roles of overfished species until they too were overfished or died of geographic realms (24). Although proxies vary epidemic diseases related to overcrowding. Retrospective data not only in precision and clarity of the signals they mea- help to clarify underlying causes and rates of ecological change, but they sure, the use of multiple proxies that give the also demonstrate achievable goals for restoration and management of same ecological signal greatly increases confi- coastal ecosystems that could not even be contemplated based on the dence in results. -
The Landing Obligation and Its Implications on the Control of Fisheries
DIRECTORATE-GENERAL FOR INTERNAL POLICIES POLICY DEPARTMENT B: STRUCTURAL AND COHESION POLICIES FISHERIES THE LANDING OBLIGATION AND ITS IMPLICATIONS ON THE CONTROL OF FISHERIES STUDY This document was requested by the European Parliament's Committee on Fisheries. AUTHORS Ocean Governance Consulting: Christopher Hedley Centre for Environment, Fisheries and Aquaculture Science: Tom Catchpole, Ana Ribeiro Santos RESPONSIBLE ADMINISTRATOR Marcus Breuer Policy Department B: Structural and Cohesion Policies European Parliament B-1047 Brussels E-mail: [email protected] EDITORIAL ASSISTANCE Adrienn Borka Lyna Pärt LINGUISTIC VERSIONS Original: EN ABOUT THE PUBLISHER To contact the Policy Department or to subscribe to its monthly newsletter please write to: [email protected] Manuscript completed in September 2015. © European Union, 2015. Print ISBN 978-92-823-7938-7 doi:10.2861/694624 QA-02-15-709-EN-C PDF ISBN 978-92-823-7939-4 doi:10.2861/303902 QA-02-15-709-EN-N This document is available on the Internet at: http://www.europarl.europa.eu/studies DISCLAIMER The opinions expressed in this document are the sole responsibility of the author and do not necessarily represent the official position of the European Parliament. Reproduction and translation for non-commercial purposes are authorized, provided the source is acknowledged and the publisher is given prior notice and sent a copy. DIRECTORATE-GENERAL FOR INTERNAL POLICIES POLICY DEPARTMENT B: STRUCTURAL AND COHESION POLICIES FISHERIES THE LANDING OBLIGATION AND ITS IMPLICATIONS ON THE CONTROL OF FISHERIES STUDY Abstract This study reviews the impacts of the new Common Fisheries Policy (CFP) rules requiring catches in regulated fisheries to be landed and counted against quotas of each Member State ("the landing obligation and requiring that catch of species subject to the landing obligation below a minimum conservation reference size be restricted to purposes other than direct human consumption. -
Are Deep-Sea Fisheries Sustainable? a Summary of New Scientific Analysis: Norse, E.A., S
RESEARCH SERIES AUGUST 2011 High biological vulnerability and economic incentives challenge the viability of deep-sea fisheries. ARE DEEP-SEA FISHERIES SUSTAINABLE? A SUMMARY OF NEW SCIENTIFIC AnaLYSIS: Norse, E.A., S. Brooke, W.W.L. Cheung, M.R. Clark, I. Ekeland, R. Froese, K.M. Gjerde, R.L. Haedrich, S.S. Heppell, T. Morato, L.E. Morgan, D. Pauly, U. R. Sumaila and R. Watson. 2012. Sustainability of Deep-sea Fisheries. Marine Policy 36(2): 307–320. AS COASTAL FISHERIES have declined around the world, fishermen have expanded their operations beyond exclusive economic zones (EEZs) to the high seas beyond EEZs, including the deep sea. Although the deep sea is the largest yet least ecologically productive part of the ocean, seamounts and other habitats can host significant amounts of some deep- sea fish species, especially when they aggregate to breed and feed. Many deep-sea fishes are slow to reproduce, or produce young only sporadically, however, making commercial fisheries unsustainable. Dr. Elliott Norse of the Marine Conservation Institute and a multidisciplinary team of co-authors analyzed data on fishes, fisheries and deep-sea biology and assessed key economic drivers and international laws to determine whether deep-sea commercial fishing could be sustainable. Ultimately, the authors conclude that most deep-sea fisheries are unsustainable, especially on the high seas. This Lenfest Research Series report is a summary of the scientists’ findings. DEEP-SEA FISHERIES As coastal fisheries have declined, fishing in the deep sea has increased. Technological advances have enabled fishing vessels to travel further from shore and locate aggregations of fish in depths that were unreachable years ago (see graphic). -
Three Simple Rules for High Catches, High Profits and Healthy Ecosystems
Three simple rules for high catches, high profits and healthy ecosystems Position paper for the round-table discussion Towards a Sustainable Fishery Sector Block 2, Interactions between Fisheries and Nature, Wednesday 23 June 2021 by Rainer Froese, GEOMAR, Kiel, Germany, [email protected] Rule 1: Do not take out more than is regrown Taking out more than is regrown is called overfishing and will shrink the fished stock below levels that can produce the maximum longterm catch (MSY). Despite the legal obligation to end overfishing in 2020, the total allowed catches (TACs) for about 40% of the stocks with suitable data in the North Sea and adjacent waters constituted overfishing (1). Overfishing is stupid: with overfishing, more effort = money is spent to get lower catches than possible at lower value and with unnecessarily high impacts on the ecosystem. The lower value is caused by overfishing shrinking the mean size of the fish and smaller fish bring lower price per kg. Impact is unnecessary high because better catches can be obtained from non- overfished stocks with less gear deployment, therefore less by-catch and less physical impact. To end overfishing, catches have to be reduced for 1-4 years, depending on current stock size. The loss caused by such reduced catches is easily regained within a few years after rebuilt stock size allows for permanent high catches at e.g. 90% of the MSY level. The 90% MSY is needed for stability; with fishing at MSY, there is a 50% chance of shrinking the stock below the MSY level and thus reducing future catches. -
Structure and Dynamics of Demersal Assemblages on the Continental Shelf and Upper Slope Off Ghana, West Africa
MARINE ECOLOGY PROGRESS SERIES Vol. 220: 1–12, 2001 Published September 27 Mar Ecol Prog Ser Structure and dynamics of demersal assemblages on the continental shelf and upper slope off Ghana, West Africa Kwame A. Koranteng* Marine Fisheries Research Division, PO Box BT-62, Tema, Ghana ABSTRACT: Using two-way indicator species analysis and detrended correspondence analysis, species on the continental shelf and upper slope of Ghana were classified into 6 assemblages. The structure of the assemblages is determined primarily by depth and type of sediment on the seabed. There are clear faunal discontinuities around 30–40, 100 and 200 m depth. The dynamics of the assemblages are influenced by physico-chemical parameters of the water masses, mainly tempera- ture, salinity and dissolved oxygen, which are periodically modified by the seasonal coastal upwelling that occurs in the area. The observed changes in the composition and relative importance of species in the assemblages can be related to increased fishing activity and environmental forcing. KEY WORDS: Species assemblages · Structure and dynamics · Continental shelf and slope · Ghana Resale or republication not permitted without written consent of the publisher INTRODUCTION nental shelf using data from the Guinean Trawling Survey (Williams 1968). In fisheries, defining the aggregation of species in In the last 3 decades, significant changes have the ecosystem is the basis for managing species by the occurred in the biological and physical components of management unit approach (Tyler et al. 1982). Caddy the Gulf of Guinea marine ecosystem and in nearshore & Sharp (1986) also pointed out that such studies are forcing factors that could have an effect on species necessary to gain a better understanding of multi- aggregations in the sub-region (Koranteng 1998). -
Production and Maximum Sustainable Yield of Fisheries Activity in Hulu Sungai Utara Regency
E3S Web of Conferences 147, 02008 (2020) https://doi.org/10.1051/e3sconf/202014702008 3rd ISMFR Production and Maximum Sustainable Yield of fisheries activity in Hulu Sungai Utara Regency Aroef Hukmanan Rais* and Tuah Nanda Merlia Wulandari Balai Riset Perikanan Perairan Umum dan Penyuluhan Perikanan, Jln. Gub. HA Bastari, No.08 Jakabaring, Palembang, Indonesia Abstract. Production and fishing activities of inland waters in the Hulu Sungai Utara Regency (HSU) have a large contribution to fulfill the food needs for the local people in South Borneo. A total of 65% of the inland waters in the HSU Regency are floodplains. This research aimed to describe the production of capture fisheries products from 2010 to 2016, the catch per unit of effort (CPUE), the estimation of maximum sustainable (MSY), the biodiversity of fish species in the flood plain waters of Hulu Sungai Utara Regency (HSU). Research and field data collection was carried out throughout 2016, by collecting fishing gears and catch data from fishermen at Tampakang Village and Palbatu Village. The highest fish production was found in 2014, which reached a value of 2053 tons/year, and tended to decline in the following year. The highest catch per unit of effort per year was found to be in 2014 (151.65 tons/effort), and significantly dropped in 2016 (36.05 tons/effort). The Maximum Sustainable Yield (MSY) analysis obtained a value of 2103.13 tons/year with an effort value of 16.57 for standard fishing gear. The research identified 31 species of fish and the largest composition was baung (Mystusnemurus) and Nila (Tilapia nilotica). -
Ecocide: the Missing Crime Against Peace'
35 690 Initiative paper from Representative Van Raan: 'Ecocide: The missing crime against peace' No. 2 INITIATIVE PAPER 'The rules of our world are laws, and they can be changed. Laws can restrict, or they can enable. What matters is what they serve. Many of the laws in our world serve property - they are based on ownership. But imagine a law that has a higher moral authority… a law that puts people and planet first. Imagine a law that starts from first do no harm, that stops this dangerous game and takes us to a place of safety….' Polly Higgins, 2015 'We need to change the rules.' Greta Thunberg, 2019 Table of contents Summary 1 1. Introduction 3 2. The ineffectiveness of current legislation 7 3. The legal framework for ecocide law 14 4. Case study: West Papua 20 5. Conclusion 25 6. Financial section 26 7. Decision points 26 Appendix: The institutional history of ecocide 29 Summary Despite all our efforts, the future of our natural environments, habitats, and ecosystems does not look promising. Human activity has ensured that climate change continues to persist. Legal instruments are available to combat this unprecedented damage to the natural living environment, but these instruments have proven inadequate. With this paper, the initiator intends to set forth an innovative new legal concept. This paper is a study into the possibilities of turning this unprecedented destruction of our natural environment into a criminal offence. In this regard, we will use the term ecocide, defined as the extensive damage to or destruction of ecosystems through human activity. -
Canales Et Al 2015
Fisheries Research 161 (2015) 261–268 Contents lists available at ScienceDirect Fisheries Research j ournal homepage: www.elsevier.com/locate/fishres Changes in the size-structure of a multispecies pelagic fishery off Northern Chile a,∗ b c,d e T. Mariella Canales , Richard Law , Rodrigo Wiff , Julia L. Blanchard a Instituto de Fomento Pesquero, Departamento de Evaluación de Recursos, Blanco 839, Valparaíso, Chile b The University of York, York Centre for Complex Systems Analysis, Ron Cooke Hub, York YO10 5EG, UK c Copas Sur-Austral, Universidad de Concepción, Departamento de Oceanografía, Barrio Universitario s/n, Chile d Center of Applied Ecology and Sustainability (CAPES), Pontificia Universidad Católica de Chile, Av. Alameda 340, Santiago, Chile e The University of Sheffield, Department of Animal and Plant Sciences, Sheffield S10 2TN, UK a r t i c l e i n f o a b s t r a c t Article history: Size-based indicators are important tools for understanding how environmental variability and fishing Received 13 February 2014 impact on marine populations and communities. Ideally, they would standardise fishery-independent Received in revised form 8 August 2014 survey data. However, this is not possible in many of the world’s ecosystems with important commercial Accepted 9 August 2014 fisheries. Using fishery-dependent data we investigated changes in the size–structure of pelagic catches off Northern Chile and whether or not these changes are influenced by the environment. We computed Keywords: single- and multispecies, size-based fishery indicators (SBFIs) from 1990 to 2008 for the main commercial Body size species, anchovy (Engraulis ringens), sardine (Sardinops sagax), jack mackerel (Trachurus murphyi) and Fishery Multispecies mackerel (Scomber japonicus). -
Welcome to Fishbase
Welcome to FishBase FishBase contains different things for different people FishBase is an information system with key data on the biology of all fishes. Similar to an encyclopedia, FishBase contains different things for different people. For example, fisheries managers will dive into the largest existing compilation of population dynamics data; teachers and students will find numerous graphs illustrating basic concepts of fish biology; conservationists will use the lists of threatened fishes for any given country; policymakers may be interested in a chronological, annotated list of introductions to their country; research scientists, as well as funding agencies, will find it useful to gain a quick overview of what is known about a certain species; zoologists and physiologists will have the largest existing compilations of fish morphology, metabolism, gill area, brain size, eye pigment, or swimming speed at their fingertips; ecologists will likewise use data on diet composition, trophic levels, food consumption and predators as inputs for their models; the fishing industry will find proximate analyses, as well as processing recommendations for many marine species; anglers will enjoy a listing of all game fishes occurring in a particular country; and scholars interested in local knowledge will find more than 300,000 common names of fishes together with the language/culture in which they are used and comments on their etymology. Unexpected usage of FishBase The above text shows the usage of FishBase that we expected when we first published it on CD- ROM and later on the Internet, in the late 1990s. That assessment has been largely correct with regard to scientific use, which led to over 5000 citations of FishBase as counted by Google Scholar. -
COVID-19 Provides an Opportunity to Advance a Sustainable UK Fisheries Policy in a Post-Brexit Brave New World
Marine Policy 120 (2020) 104114 Contents lists available at ScienceDirect Marine Policy journal homepage: http://www.elsevier.com/locate/marpol Short communication COVID-19 provides an opportunity to advance a sustainable UK fisheries policy in a post-Brexit brave new world Paul S. Kemp a,*, Rainer Froese b, Daniel Pauly c a International Centre for Ecohydraulics Research, Faculty of Engineering and the Physical Sciences, Southampton Boldrewood Innovation Campus, University of Southampton, SO16 7QF, UK b GEOMAR Helmholtz Centre for Ocean Research, 24105, Kiel, Germany c Institute for the Oceans and Fisheries, The University of British Columbia, 2202 Main Mall, Vancouver, B.C., V6T 1Z4, Canada ARTICLE INFO ABSTRACT Keywords: Brexit creates a systemic shock that provides a unique opportunity for the UK to implement a new sustainable Ocean harvest Fisheries Policy to better manage the multiple stocks on which future fisherswill depend on leaving the European European union fisheries policy Union. At the same time, the global slowdown of commercial fishing as a result of COVID-19 has reduced Marine fisheries management pressure on some threatened stocks to levels not seen since the Second World War. In combination, Brexit and the Water-energy-fisheries Nexus COVID-19 slowdown have created a unique opportunity to facilitate the recovery of a threatened resource. Nevertheless, challenges remain as fisheries represent only 0.12% of UK economic output, presenting a risk that opportunities for more sustainable management will be lost during wider -
Seafood Watch® Standard for Fisheries
1 Seafood Watch® Standard for Fisheries Table of Contents Table of Contents ............................................................................................................................... 1 Introduction ...................................................................................................................................... 2 Seafood Watch Guiding Principles ...................................................................................................... 3 Seafood Watch Criteria and Scoring Methodology for Fisheries ........................................................... 5 Criterion 1 – Impacts on the Species Under Assessment ...................................................................... 8 Factor 1.1 Abundance .................................................................................................................... 9 Factor 1.2 Fishing Mortality ......................................................................................................... 19 Criterion 2 – Impacts on Other Capture Species ................................................................................ 22 Factor 2.1 Abundance .................................................................................................................. 26 Factor 2.2 Fishing Mortality ......................................................................................................... 27 Factor 2.3 Modifying Factor: Discards and Bait Use .................................................................... 29 Criterion