Models for an Ecosystem Approach to Fisheries
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SUSTAINABLE FISHERIES and RESPONSIBLE AQUACULTURE: a Guide for USAID Staff and Partners
SUSTAINABLE FISHERIES AND RESPONSIBLE AQUACULTURE: A Guide for USAID Staff and Partners June 2013 ABOUT THIS GUIDE GOAL This guide provides basic information on how to design programs to reform capture fisheries (also referred to as “wild” fisheries) and aquaculture sectors to ensure sound and effective development, environmental sustainability, economic profitability, and social responsibility. To achieve these objectives, this document focuses on ways to reduce the threats to biodiversity and ecosystem productivity through improved governance and more integrated planning and management practices. In the face of food insecurity, global climate change, and increasing population pressures, it is imperative that development programs help to maintain ecosystem resilience and the multiple goods and services that ecosystems provide. Conserving biodiversity and ecosystem functions are central to maintaining ecosystem integrity, health, and productivity. The intent of the guide is not to suggest that fisheries and aquaculture are interchangeable: these sectors are unique although linked. The world cannot afford to neglect global fisheries and expect aquaculture to fill that void. Global food security will not be achievable without reversing the decline of fisheries, restoring fisheries productivity, and moving towards more environmentally friendly and responsible aquaculture. There is a need for reform in both fisheries and aquaculture to reduce their environmental and social impacts. USAID’s experience has shown that well-designed programs can reform capture fisheries management, reducing threats to biodiversity while leading to increased productivity, incomes, and livelihoods. Agency programs have focused on an ecosystem-based approach to management in conjunction with improved governance, secure tenure and access to resources, and the application of modern management practices. -
Fishers and Fish Traders of Lake Victoria: Colonial
FISHERS AND FISH TRADERS OF LAKE VICTORIA: COLONIAL POLICY AND THE DEVELOPMENT OF FISH PRODUCTION IN KENYA, 1880-1978. by PAUL ABIERO OPONDO Student No. 34872086 submitted in accordance with the requirement for the degree of DOCTOR OF LITERATURE AND PHILOSOPHY in the subject HISTORY at the UNIVERSITY OF SOUTH AFRICA PROMOTER: DR. MUCHAPARARA MUSEMWA, University of the Witwatersrand CO-PROMOTER: PROF. LANCE SITTERT, University of Cape Town 10 February 2011 DECLARATION I declare that ‘Fishers and Fish Traders of Lake Victoria: Colonial Policy and the Development of Fish Production in Kenya, 1895-1978 ’ is my original unaided work and that all the sources that I have used or quoted have been indicated and acknowledged by means of complete references. I further declare that the thesis has never been submitted before for examination for any degree in any other university. Paul Abiero Opondo __________________ _ . 2 DEDICATION This work is dedicated to several fishers and fish traders who continue to wallow in poverty and hopelessness despite their daily fishing voyages, whose sweat and profits end up in the pockets of big fish dealers and agents from Nairobi. It is equally dedicated to my late father, Michael, and mother, Consolata, who guided me with their wisdom early enough. In addition I dedicate it to my loving wife, Millicent who withstood the loneliness caused by my occasional absence from home, and to our children, Nancy, Michael, Bivinz and Barrack for whom all this is done. 3 ABSTRACT The developemnt of fisheries in Lake Victoria is faced with a myriad challenges including overfishing, environmental destruction, disappearance of certain indigenous species and pollution. -
Purification of Glucose 6-Phosphate Dehydrogenase From
MARINE SCIENCE AND TECHNOLOGY BULLETIN VOLUME: 9 ISSUE: 2 DECEMBER 2020 Editor-in-Chief Adem Yavuz Sönmez Kastamonu University, Turkey Co-Editor Semih Kale Çanakkale Onsekiz Mart University, Turkey Section Editors Soner Bilen Kastamonu University, Turkey Ertuğrul Terzi Kastamonu University, Turkey Ali Eslem Kadak Kastamonu University, Turkey Gökhan Arslan Atatürk University, Turkey Statistics Editor Aycan Mutlu Yağanoğlu Atatürk University, Turkey Foreign Language Editor Muhammet Sinan Alpsoy Kastamonu University, Turkey Editorial Board Agus Oman Sudrajat Institut Pertanian Bogor, Indonesia Anca Nicoleta Şuţan University of Piteşti, Romania Antanas Kontautas Klaipeda University, Lithuania Arya Vazirzadeh Shiraz University, Iran Barış Bayraklı Sinop University, Turkey Derya Güroy Yalova University, Turkey Fazıl Şen Yüzüncü Yıl University, Turkey Gouranga Biswas Kakdwip Research Centre of Central Institute, India Hasan Hüseyin Atar Ankara University, Turkey İlhan Altınok Karadeniz Technical University, Turkey Liliana Török Danube Delta National Institute for Research & Development, Romania Mahmut Elp Kastamonu University, Turkey Marina Alexandrovna Sazykina Southern Federal University, Russia Mehmet Gökoğlu Akdeniz University, Turkey Muhammad Naeem Khan University of the Punjab, Pakistan Sajmir Beqiraj University of Tirana, Albania Sefa Acarlı Çanakkale Onsekiz Mart University, Turkey Sitti Zayda B. Halun Mindanao State University, Philippines Sonya Uzunova Institute of Fishing Resources, Bulgaria Süleyman Özdemir Sinop University, Turkey -
An Assessment of Marine Ecosystem Damage from the Penglai 19-3 Oil Spill Accident
Journal of Marine Science and Engineering Article An Assessment of Marine Ecosystem Damage from the Penglai 19-3 Oil Spill Accident Haiwen Han 1, Shengmao Huang 1, Shuang Liu 2,3,*, Jingjing Sha 2,3 and Xianqing Lv 1,* 1 Key Laboratory of Physical Oceanography, Ministry of Education, Ocean University of China, Qingdao 266100, China; [email protected] (H.H.); [email protected] (S.H.) 2 North China Sea Environment Monitoring Center, State Oceanic Administration (SOA), Qingdao 266033, China; [email protected] 3 Department of Environment and Ecology, Shandong Province Key Laboratory of Marine Ecology and Environment & Disaster Prevention and Mitigation, Qingdao 266100, China * Correspondence: [email protected] (S.L.); [email protected] (X.L.) Abstract: Oil spills have immediate adverse effects on marine ecological functions. Accurate as- sessment of the damage caused by the oil spill is of great significance for the protection of marine ecosystems. In this study the observation data of Chaetoceros and shellfish before and after the Penglai 19-3 oil spill in the Bohai Sea were analyzed by the least-squares fitting method and radial basis function (RBF) interpolation. Besides, an oil transport model is provided which considers both the hydrodynamic mechanism and monitoring data to accurately simulate the spatial and temporal distribution of total petroleum hydrocarbons (TPH) in the Bohai Sea. It was found that the abundance of Chaetoceros and shellfish exposed to the oil spill decreased rapidly. The biomass loss of Chaetoceros and shellfish are 7.25 × 1014 ∼ 7.28 × 1014 ind and 2.30 × 1012 ∼ 2.51 × 1012 ind in the area with TPH over 50 mg/m3 during the observation period, respectively. -
Redacted for Privacy Abstract Approved: I
AN ABSTRACT OF THE THESIS OF Nilton Eduardo Deza Arroyo for the degree of Master of Science in Fisheries Science presented on November 8. 1996. Title: Mercury Accumulation in Fish from Madre de Dios. a Goidmining Area in the Amazon Basin. Peru Redacted for Privacy Abstract approved: I. Weber Redacted for Privacy Wayne K. Seim In this study mercury contamination from goldmining was measured in tissues of fish from Madre de Dios, Amazonia, Peru.Bioaccumulation, biomagnification, the difference in mercury burden among residential and migratory species, and comparison between fish from Puerto Maldonado (a goidmining area) and Manu (a pristine area) were examined. Samples of dorsal-epaxial muscle of dorado (Brachyplatystoma flavicans); fasaco (Hoplias malabaricus),bothcarnivores;boquichico(Prochilodusnigricans),a detritivore;mojarita (Bryconopsaffmelanurus),an insectivore;and carachama (Hypostomus sp.), an detntivore; were analyzed by using the flameless cold vapor atomic absorption spectrophotometry technique. Dorado, a top predator, displayed the highest values of total mercury (699 ugfKg ± 296).Six out of ten dorados showed an average higher than safe values of 0.5 ug/g (WHO, 1991). Lower values reported in this study in the other species suggest that dorado may have gained its mercury burden downstream of Madre de Dios River, in the Madeira River, where goidmining activities are several times greater than that in the Madre de Dios area. Fasaco from Puerto Maldonado displayed higher levels than fasaco from Manu; however, mercury contamination in Puerto Maldonado is lower than values reported for fish from areas with higher quantities of mercury released into the environment. Positive correlation between mercury content and weight of fish for dorado, fasaco and boquichico served to explain bioaccumulation processes in the area of study. -
Sustainable Seafood Campaign
Sustainable Seafood Campaign Overfishing and destructive fishing are among the most significant threats facing our oceans. The UN reports that three-quarters of global fish stocks are either fully exploited or overexploited. Scientists estimate that 90% of top marine predators such as tuna and sharks are already gone. Pirate fishing, estimated to account for up to a third of the global catch, is notorious for targeting at-risk populations and using highly destructive methods. Destructive fishing indiscriminately kills “non-target” species, including marine mammals and seabirds, and destroys habitats that marine species depend on for survival. In addition to the direct and cascading effects on marine ecosystems, overfishing and destructive fishing make our ocean ecosystems more vulnerable to global warming. If current trends continue, scientists predict global fisheries will collapse in forty years. U.S. consumers buy half their seafood at supermarkets, to the tune of $16 billion every year. As consumer interest in sustainable products has grown, so have retailer efforts to promote their eco-friendly initiatives. Yet, few supermarkets have made significant efforts to improve their seafood sustainability. Greenpeace is calling on supermarkets to sell only sustainable seafood and to support positive reforms in fisheries management. By doing so, supermarkets will do their part to help avert the crisis facing our oceans while ensuring their customers quality fish from sustainable fisheries for years to come. Supermarkets have enormous purchasing power, and are well positioned to influence the way the fishing industry operates. What You Can Do! Greenpeace needs your help monitoring supermarket seafood policies and practices. The information you gather will be used to update our supermarket scorecard. -
Vegetation Demographics in Earth System Models: a Review of Progress and Priorities
Lawrence Berkeley National Laboratory Recent Work Title Vegetation demographics in Earth System Models: A review of progress and priorities. Permalink https://escholarship.org/uc/item/3912p4m3 Journal Global change biology, 24(1) ISSN 1354-1013 Authors Fisher, Rosie A Koven, Charles D Anderegg, William RL et al. Publication Date 2018 DOI 10.1111/gcb.13910 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Received: 11 April 2017 | Revised: 12 August 2017 | Accepted: 17 August 2017 DOI: 10.1111/gcb.13910 RESEARCH REVIEW Vegetation demographics in Earth System Models: A review of progress and priorities Rosie A. Fisher1 | Charles D. Koven2 | William R. L. Anderegg3 | Bradley O. Christoffersen4 | Michael C. Dietze5 | Caroline E. Farrior6 | Jennifer A. Holm2 | George C. Hurtt7 | Ryan G. Knox2 | Peter J. Lawrence1 | Jeremy W. Lichstein8 | Marcos Longo9 | Ashley M. Matheny10 | David Medvigy11 | Helene C. Muller-Landau12 | Thomas L. Powell2 | Shawn P. Serbin13 | Hisashi Sato14 | Jacquelyn K. Shuman1 | Benjamin Smith15 | Anna T. Trugman16 | Toni Viskari12 | Hans Verbeeck17 | Ensheng Weng18 | Chonggang Xu4 | Xiangtao Xu19 | Tao Zhang8 | Paul R. Moorcroft20 1National Center for Atmospheric Research, Boulder, CO, USA 2Lawrence Berkeley National Laboratory, Berkeley, CA, USA 3Department of Biology, University of Utah, Salt Lake City, UT, USA 4Los Alamos National Laboratory, Los Alamos, NM, USA 5Department of Earth and Environment, Boston University, Boston, MA, USA 6Department of Integrative Biology, -
Emergent Biogeography of Microbial Communities in a Model Ocean
REPORTS germ insects not only uncovers those features es- mRNA localization indeed appears to be an sential to this developmental mode but also sheds important component of long-germ embryogene- light on how the bcd-dependent anterior patterning sis, perhaps even playing a role in the transition program might have evolved. Through analysis of from the ancestral short-germ to the derived long- the regulation of the trunk gap gene Kr in Dro- germ fate. sophila and Nasonia,wehavebeenabletodem- onstrate that anterior repression of Kr is essential References and Notes for head and thorax formation and is a common 1. G. K. Davis, N. H. Patel, Annu. Rev. Entomol. 47, 669 (2002). feature of long-germ patterning. Both insects 2. T. Berleth et al., EMBO J. 7, 1749 (1988). accomplish this task through maternal, anteriorly 3. W. Driever, C. Nusslein-Volhard, Cell 54, 83 (1988). localized factors that either indirectly (Drosophila) 4. J. Lynch, C. Desplan, Curr. Biol. 13, R557 (2003). or directly (Nasonia) repress Kr and, hence, trunk 5. J. A. Lynch, A. E. Brent, D. S. Leaf, M. A. Pultz, C. Desplan, Nature 439, 728 (2006). fates. In Drosophila, the terminal system and bcd 6. J. Savard et al., Genome Res. 16, 1334 (2006). regulate expression of gap genes, including Dm-gt, 7. G. Struhl, P. Johnston, P. A. Lawrence, Cell 69, 237 (1992). that repress Dm-Kr. Nasonia’s bcd-independent 8. A. Preiss, U. B. Rosenberg, A. Kienlin, E. Seifert, long-germ embryos must solve the same problem, H. Jackle, Nature 313, 27 (1985). Fig. 4. -
Meta-Ecosystems: a Theoretical Framework for a Spatial Ecosystem Ecology
Ecology Letters, (2003) 6: 673–679 doi: 10.1046/j.1461-0248.2003.00483.x IDEAS AND PERSPECTIVES Meta-ecosystems: a theoretical framework for a spatial ecosystem ecology Abstract Michel Loreau1*, Nicolas This contribution proposes the meta-ecosystem concept as a natural extension of the Mouquet2,4 and Robert D. Holt3 metapopulation and metacommunity concepts. A meta-ecosystem is defined as a set of 1Laboratoire d’Ecologie, UMR ecosystems connected by spatial flows of energy, materials and organisms across 7625, Ecole Normale Supe´rieure, ecosystem boundaries. This concept provides a powerful theoretical tool to understand 46 rue d’Ulm, F–75230 Paris the emergent properties that arise from spatial coupling of local ecosystems, such as Cedex 05, France global source–sink constraints, diversity–productivity patterns, stabilization of ecosystem 2Department of Biological processes and indirect interactions at landscape or regional scales. The meta-ecosystem Science and School of perspective thereby has the potential to integrate the perspectives of community and Computational Science and Information Technology, Florida landscape ecology, to provide novel fundamental insights into the dynamics and State University, Tallahassee, FL functioning of ecosystems from local to global scales, and to increase our ability to 32306-1100, USA predict the consequences of land-use changes on biodiversity and the provision of 3Department of Zoology, ecosystem services to human societies. University of Florida, 111 Bartram Hall, Gainesville, FL Keywords 32611-8525, -
Towards a Sustainable Fishery: the Price-Cap Approach
Towards a Sustainable Fishery: The Price-Cap Approach Eric M. Singer* Overfishing is the classic tragedy of the commons. So far, governments have pursued a variety of solutions to incentivize sustainable commercial fishing practices, realizing only mixed results. After describing the costs associated with implementing overfishing controls, I propose a new method of regulating commercial fishing: the price cap. This Article explains the theory of how price caps can incentivize sustainable fishing, analyzes the implementation costs associated with price caps, and compares price caps to existing overfishing regulations. Because each fishery is unique, no single method will produce the greatest benefit at the lowest cost in all fisheries. Accordingly, I analyze the factors that might make a fishery a better or worse candidate for the implementation of price caps. I. INTRODUCTION ................................................................................. 254 II. COSTS OF REGULATION .................................................................... 260 A. Transaction Costs ............................................................. 261 B. Enforcement Costs ............................................................ 263 C. Political Costs ................................................................... 265 D. International Cooperation ................................................. 266 E. Substitution Costs ............................................................. 267 F. Skill-Misallocation Costs ................................................ -
Chapter 4 – Steady State Models
CHAPTER 4 Steady State Models X.-Z. Kong, F.-L. Xu1, W. He, W.-X. Liu, B. Yang Peking University, Beijing, China 1Corresponding author: E-mail: xufl@urban.pku.edu.cn OUTLINE 4.1 Steady State Model: Ecopath as an 4.2.4.2 Changes in Ecosystem Example 66 Functioning 79 4.1.1 Steady State Model 66 4.2.4.3 Collapse in the Food 4.1.2 Ecopath Model 66 Web: Differences in 4.1.3 Future Perspectives 68 Structure 81 4.2.4.4 Toward an Immature 4.2 Ecopath Model for a Large Chinese but Stable Ecosystem 83 Lake: A Case Study 68 4.2.4.5 Potential Driving 4.2.1 Introduction 68 Factors and 4.2.2 Study Site 70 Underlying 4.2.3 Model Development 73 Mechanisms 84 4.2.3.1 Model Construction 4.2.4.6 Hints for Future Lake and Parameterization 73 Fishery and 4.2.3.2 Evaluation of Ecosystem Restoration 85 Functioning 74 4.2.3.3 Determination of 4.3 Conclusions 86 Trophic Level 76 References 86 4.2.4 Results and Discussion 76 4.2.4.1 Basic Model Performance 76 Ecological Model Types, Volume 28 Ó 2016 Elsevier B.V. http://dx.doi.org/10.1016/B978-0-444-63623-2.00004-9 65 All rights reserved. 66 4. STEADY STATE MODELS 4.1 STEADY STATE MODEL: ECOPATH AS AN EXAMPLE 4.1.1 Steady State Model Steady state ecological models are established to describe conditions in which the modeled components (mass or energy) are stable, i.e., do not change over time (Jørgensen and Fath, 2011). -
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