6 North Sea 6.1 Ecosystem Overview 6.1.1 Ecosystem Components
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Shrimp Fishing in Mexico
235 Shrimp fishing in Mexico Based on the work of D. Aguilar and J. Grande-Vidal AN OVERVIEW Mexico has coastlines of 8 475 km along the Pacific and 3 294 km along the Atlantic Oceans. Shrimp fishing in Mexico takes place in the Pacific, Gulf of Mexico and Caribbean, both by artisanal and industrial fleets. A large number of small fishing vessels use many types of gear to catch shrimp. The larger offshore shrimp vessels, numbering about 2 212, trawl using either two nets (Pacific side) or four nets (Atlantic). In 2003, shrimp production in Mexico of 123 905 tonnes came from three sources: 21.26 percent from artisanal fisheries, 28.41 percent from industrial fisheries and 50.33 percent from aquaculture activities. Shrimp is the most important fishery commodity produced in Mexico in terms of value, exports and employment. Catches of Mexican Pacific shrimp appear to have reached their maximum. There is general recognition that overcapacity is a problem in the various shrimp fleets. DEVELOPMENT AND STRUCTURE Although trawling for shrimp started in the late 1920s, shrimp has been captured in inshore areas since pre-Columbian times. Magallón-Barajas (1987) describes the lagoon shrimp fishery, developed in the pre-Hispanic era by natives of the southeastern Gulf of California, which used barriers built with mangrove sticks across the channels and mouths of estuaries and lagoons. The National Fisheries Institute (INP, 2000) and Magallón-Barajas (1987) reviewed the history of shrimp fishing on the Pacific coast of Mexico. It began in 1921 at Guaymas with two United States boats. -
The Dutch Case
The Dutch Case A Network of Marine Protected Areas The Dutch Case – A Network of Marine ProtectedEmilie Areas Hugenholtz Abbreviations BALANCE Baltic Sea Management: Nature Conservation and Sustainable Development of the Ecosystem through Spatial Planning BPA(s) Benthic Protection Areas CFP Common Fisheries Policy EEZ Exclusive Economic Zone EC European Commission EU European Union HP Horse Power HELCOM Regional Sea Convention for the Baltic Area IBN 2015 The Integrated Management Plan for the North Sea 2015 ICES International Council for the Exploration of the Sea IMARES Institute for Marine Resources and Ecosystem Studies IUCN International Union for Conservation of Nature Lundy MNR Lundy Marine Nature Reserve MESH (Development of a Framework for) Mapping European Seabed Habitats MPA(s) Marine Protected Area(s) NM Nautical Mile (1.852 km) NGO(s) Non-Governmental Organisation(s) OSPAR Convention on the Protection of the Marine Environment of the North-East Atlantic RFMOs Regional Fisheries Management Organisations SACs Special Areas of Conservation under 92/43 Habitats Directive SCI Site of Community Importance SPAs Special Protected Area under 79/409 Birds Directive SSB Spawning Stock Biomass t Ton (1,000 kilo) TRAC Transboundary Resources Assessment Committee (USA/Canada) WWF World Wide Fund for Nature Cover Illustration (left) North Sea wave breakers in Cadzand, The Netherlands Cover Illustration (right) White-bellied monkfish (Lophius piscatorius) is a predominant species in the northern North Sea. Common along the entire Norwegian -
Fronts in the World Ocean's Large Marine Ecosystems. ICES CM 2007
- 1 - This paper can be freely cited without prior reference to the authors International Council ICES CM 2007/D:21 for the Exploration Theme Session D: Comparative Marine Ecosystem of the Sea (ICES) Structure and Function: Descriptors and Characteristics Fronts in the World Ocean’s Large Marine Ecosystems Igor M. Belkin and Peter C. Cornillon Abstract. Oceanic fronts shape marine ecosystems; therefore front mapping and characterization is one of the most important aspects of physical oceanography. Here we report on the first effort to map and describe all major fronts in the World Ocean’s Large Marine Ecosystems (LMEs). Apart from a geographical review, these fronts are classified according to their origin and physical mechanisms that maintain them. This first-ever zero-order pattern of the LME fronts is based on a unique global frontal data base assembled at the University of Rhode Island. Thermal fronts were automatically derived from 12 years (1985-1996) of twice-daily satellite 9-km resolution global AVHRR SST fields with the Cayula-Cornillon front detection algorithm. These frontal maps serve as guidance in using hydrographic data to explore subsurface thermohaline fronts, whose surface thermal signatures have been mapped from space. Our most recent study of chlorophyll fronts in the Northwest Atlantic from high-resolution 1-km data (Belkin and O’Reilly, 2007) revealed a close spatial association between chlorophyll fronts and SST fronts, suggesting causative links between these two types of fronts. Keywords: Fronts; Large Marine Ecosystems; World Ocean; sea surface temperature. Igor M. Belkin: Graduate School of Oceanography, University of Rhode Island, 215 South Ferry Road, Narragansett, Rhode Island 02882, USA [tel.: +1 401 874 6533, fax: +1 874 6728, email: [email protected]]. -
Fishery Announcement Template V2.1 (29Th April 2019) (Based on MSC Fishery Announcement Template V2.01)
Control Union Pesca Ltd. CFTO Indian Ocean Purse Seine Skipjack fishery MSC Fishery Announcement Control Union Pesca Ltd 56 High Street, Lymington, Hampshire, SO41 9AH, United Kingdom Tel: 01590 613007 Fax: 01590 671573 Email: [email protected] Website: www.cupesca.com Marine Stewardship Council fishery announcement Table 1 – Fishery announcement 1 Fishery name CFTO Indian Ocean Purse Seine Skipjack fishery 2 Assessment number Initial assessment 3 Reduced reassessment (Yes/No) N/A 4 Statement that the fishery is within scope The CAB confirms that the fishery entering full assessment meets the scope requirements (FCR 7.4) for MSC fishery assessments [FCR 7.8.3.1]. The CAB further confirms the following: • The fishery is within scope of the MSC standard, i.e. it does not operate under a controversial unilateral exemption to an international agreement, use destructive fishing practices, target amphibians, birds, reptiles or mammals and is not overwhelmed by dispute; • The CAB has reviewed available assessment reports and other information. A pre-assessment was conducted for this fishery (February 2019); • The fishery has not failed an assessment within the last two years; • IPI stocks are not caught; • The fishery is enhanced; • The fishery is not based on an introduced species; and • The fishery does not include an entity that has been successfully prosecuted for violations against forced labour laws. The fishery overlaps with the “Maldives pole & line skipjack tuna” and “Echebastar Indian Ocean purse seine skipjack tuna” 5 Unit(s) -
Ecological Modelling 321 (2016) 35–45
Ecological Modelling 321 (2016) 35–45 Contents lists available at ScienceDirect Ecological Modelling journa l homepage: www.elsevier.com/locate/ecolmodel Modelling the effects of fishing on the North Sea fish community size composition a,∗ b a Douglas C. Speirs , Simon P.R. Greenstreet , Michael R. Heath a Department of Mathematics and Statistics, University of Strathclyde, Glasgow G1 1XH, UK b Marine Scotland Science, Marine Laboratory, PO Box 101, 375 Victoria Road, Aberdeen AB11 9DB, UK a r a t i b s c t l e i n f o r a c t Article history: Ecosystem-based management of the North Sea demersal fish community uses the large fish indicator Received 18 March 2015 (LFI), defined as the proportion by weight of fish caught in the International Bottom Trawl Survey (IBTS) Received in revised form 23 October 2015 exceeding a length of 40 cm. Current values of the LFI are ∼0.15, but the European Union (EU) Marine Accepted 27 October 2015 Strategy Framework Directive (MSFD) requires a value of 0.3 be reached by 2020. An LFI calculated from an eight-species subset correlated closely with the full community LFI, thereby permitting an exploration Keywords: of the effects of various fishing scenarios on projected values of the LFI using an extension of a previously Length-structured population model published multi-species length-structured model that included these key species. The model replicated Multi-species model historical changes in biomass and size composition of individual species, and generated an LFI that was North Sea ∼ Fisheries significantly correlated with observations. -
EUROPEAN COMMISSION Brussels, 18.9.2020 SWD(2020)
EUROPEAN COMMISSION Brussels, 18.9.2020 SWD(2020) 206 final COMMISSION STAFF WORKING DOCUMENT REGIONAL SEA BASIN ANALYSES REGIONAL CHALLENGES IN ACHIEVING THE OBJECTIVES OF THE COMMON FISHERIES POLICY – A SEA BASIN PERSPECTIVE TO GUIDE EMFF PROGRAMMING EN EN Contents INTRODUCTION ...................................................................................................................................... 5 1 Reducing the impacts of fishing on ecosystems ............................................................................. 7 1.1 Reducing fishing pressure ........................................................................................................... 7 1.2 Managing the landing obligation on board and on land............................................................. 8 1.3 Preserving ecosystems through environmental legislation ........................................................ 8 2 Providing conditions for an economically viable and competitive fishing sector and contributing to a fair standard of living for those who depend on fishing activities ................................................ 10 2.1 Addressing overcapacity ........................................................................................................... 10 2.2 Consolidating economic and social performance ..................................................................... 10 2.3 Estimation of the impact of COVID-19 crisis on the fisheries sector ........................................ 11 3 Improving enforcement and control -
Offshore Wind Submarine Cabling Overview Fisheries Technical Working Group
OFFSHOREoverview WIND SUBMARINE CABLING Fisheries Technical Working Group Final Report | Report Number 21-14 | April 2021 NYSERDA’s Promise to New Yorkers: NYSERDA provides resources, expertise, and objective information so New Yorkers can make confident, informed energy decisions. Our Vision: New York is a global climate leader building a healthier future with thriving communities; homes and businesses powered by clean energy; and economic opportunities accessible to all New Yorkers. Our Mission: Advance clean energy innovation and investments to combat climate change, improving the health, resiliency, and prosperity of New Yorkers and delivering benefits equitably to all. Courtesy, Equinor, Dudgeon Offshore Wind Farm Offshore Wind Submarine Cabling Overview Fisheries Technical Working Group Final Report Prepared for: New York State Energy Research and Development Authority Albany, NY Morgan Brunbauer Offshore Wind Marine Fisheries Manager Prepared by: Tetra Tech, Inc. Boston, MA Brian Dresser Director of Fisheries Programs NYSERDA Report 21-14 NYSERDA Contract 111608A April 2021 Notice This report was prepared by Tetra Tech, Inc. in the course of performing work contracted for and sponsored by the New York State Energy Research and Development Authority (hereafter “NYSERDA”). The opinions expressed in this report do not necessarily reflect those of NYSERDA or the State of New York, and reference to any specific product, service, process, or method does not constitute an implied or expressed recommendation or endorsement of it. Further, NYSERDA, the State of New York, and the contractor make no warranties or representations, expressed or implied, as to the fitness for particular purpose or merchantability of any product, apparatus, or service, or the usefulness, completeness, or accuracy of any processes, methods, or other information contained, described, disclosed, or referred to in this report. -
Report of the Working Group on Fish Technology and Fish
ICES WGFTFB REPORT 2016 SCICOM/ACOM STEERING GROUP ON INTEGRATED ECOSYSTEM OBSERVATION AND MONITORING ICES CM 2016/SSGIEOM:22 REF. ACOM AND SCICOM Report of the Working Group on Fishing Technology and Fish Behaviour (WGFTFB) 25-29 April 2016 Merida, Mexico International Council for the Exploration of the Sea Conseil International pour l’Exploration de la Mer H. C. Andersens Boulevard 44–46 DK-1553 Copenhagen V Denmark Telephone (+45) 33 38 67 00 Telefax (+45) 33 93 42 15 www.ices.dk [email protected] Recommended format for purposes of citation: ICES. 2016. Report of the Working Group on Fishing Technology and Fish Behaviour (WGFTFB), 25-29 April 2016, Merida, Mexico. ICES CM 2016/SSGIEOM:22. 183 pp. For permission to reproduce material from this publication, please apply to the Gen- eral Secretary. The document is a report of an Expert Group under the auspices of the International Council for the Exploration of the Sea and does not necessarily represent the views of the Council. © 2016 International Council for the Exploration of the Sea ICES WGFTFB REPORT 2016 | i Contents Executive Summary ............................................................................................................... 1 1 Administrative details .................................................................................................... 4 2 Introduction ...................................................................................................................... 5 3 Terms of Reference......................................................................................................... -
Collapse and Recovery of Marine Fishes
letters to nature sulphide complexes, indicating that Cu sulphide clusters are more 7. Al-Farawati, R. & van den Berg, C. M. G. Metal-sulfide complexation in seawater. Mar. Chem. 63, 331–352 (1999). stable than Cu organic complexes. This explains why laboratory 8. Luther III, G. W., Rickard, D. T., Theberge, S. M. & Olroyd, A. Determination of metal (bi)sulfide cultures of oceanic phytoplankton have been observed to increase stability constants of Mn2+,Fe2+,Co2+,Ni2+,Cu2+, and Zn2+ by voltammetric methods. Environ. Sci. the production of total dissolved sulphides when the concentrations Technol. 30, 671–679 (1996). of free Cu and Zn in the culture media were increased22. Although 9. Helz, G. R, Charnock, J. M., Vaughan, D. J. & Garner, C. D. Multinuclearity of aqueous copper and zinc bisulfide complexes—an EXAFS investigation. Geochim. Cosmochim. Acta 57, the data that we report here suggest that metal sulphide formation is 15–25 (1993). a means of detoxifying trace metals for organisms, further toxico- 10. Luther III, G. W., Theberge, S. M. & Rickard, D. T. Evidence for aqueous clusters as intermediates logical studies are needed to quantify the roles both sulphides and during zinc sulfide formation. Geochim. Cosmochim. Acta 19/20, 3159–3169 (1999). ‘natural’ organic ligands play in controlling Cu toxicity in natural 11. Peters, J. W., Lanzilotta, W. N., Lemon, B. J. & Seefeldt, L. C. X-ray crystal structure of the Fe-only hydrogenase (Cpl) from Clostridium pasteurianum to 1.8 angstrom resolution. Science 282, 1853– waters. 1858 (1998). Sulphur complexation may have a dramatic effect on the acute 12. -
Natura 2000 Sites for Reefs and Submerged Sandbanks Volume II: Northeast Atlantic and North Sea
Implementation of the EU Habitats Directive Offshore: Natura 2000 sites for reefs and submerged sandbanks Volume II: Northeast Atlantic and North Sea A report by WWF June 2001 Implementation of the EU Habitats Directive Offshore: Natura 2000 sites for reefs and submerged sandbanks A report by WWF based on: "Habitats Directive Implementation in Europe Offshore SACs for reefs" by A. D. Rogers Southampton Oceanographic Centre, UK; and "Submerged Sandbanks in European Shelf Waters" by Veligrakis, A., Collins, M.B., Owrid, G. and A. Houghton Southampton Oceanographic Centre, UK; commissioned by WWF For information please contact: Dr. Sarah Jones WWF UK Panda House Weyside Park Godalming Surrey GU7 1XR United Kingdom Tel +441483 412522 Fax +441483 426409 Email: [email protected] Cover page photo: Trawling smashes cold water coral reefs P.Buhl-Mortensen, University of Bergen, Norway Prepared by Sabine Christiansen and Sarah Jones IMPLEMENTATION OF THE EU HD OFFSHORE REEFS AND SUBMERGED SANDBANKS NE ATLANTIC AND NORTH SEA TABLE OF CONTENTS TABLE OF CONTENTS ACKNOWLEDGEMENTS I LIST OF MAPS II LIST OF TABLES III 1 INTRODUCTION 1 2 REEFS IN THE NORTHEAST ATLANTIC AND THE NORTH SEA (A.D. ROGERS, SOC) 3 2.1 Data inventory 3 2.2 Example cases for the type of information provided (full list see Vol. IV ) 9 2.2.1 "Darwin Mounds" East (UK) 9 2.2.2 Galicia Bank (Spain) 13 2.2.3 Gorringe Ridge (Portugal) 17 2.2.4 La Chapelle Bank (France) 22 2.3 Bibliography reefs 24 2.4 Analysis of Offshore Reefs Inventory (WWF)(overview maps and tables) 31 2.4.1 North Sea 31 2.4.2 UK and Ireland 32 2.4.3 France and Spain 39 2.4.4 Portugal 41 2.4.5 Conclusions 43 3 SUBMERGED SANDBANKS IN EUROPEAN SHELF WATERS (A. -
Dogger Bank Special Area of Conservation (SAC) MMO Fisheries Assessment 2021
Document Control Title Dogger Bank Special Area of Conservation (SAC) MMO Fisheries Assessment 2021 Authors T Barnfield; E Johnston; T Dixon; K Saunders; E Siegal Approver(s) V Morgan; J Duffill Telsnig; N Greenwood Owner T Barnfield Revision History Date Author(s) Version Status Reason Approver(s) 19/06/2020 T Barnfield; V.A0.1 Draft Introduction and Part V Morgan E Johnston A 06/07/2020 T Barnfield; V.A0.2 Draft Internal QA of V Morgan E Johnston Introduction and Part A 07/07/2020 T Barnfield; V.A0.3 Draft JNCC QA of A Doyle E Johnston Introduction and Part A 14/07/2020 T Barnfield; V.A0.4 Draft Introduction and Part V Morgan E Johnston A JNCC comments 26/07/2020 T Barnfield; V.BC0.1 Draft Part B & C N Greenwood E Johnston 29/07/2020 T Barnfield; V.BC0.2 Draft Internal QA of Part B N Greenwood E Johnston & C 30/07/2020 T Barnfield; V.BC0.3 Draft JNCC QA of A Doyle E Johnston Introduction and Part A 05/08/2020 T Barnfield; V.BC0.4 Draft Part B & C JNCC N Greenwood E Johnston comments 06/08/2020 T Barnfield; V.1.0 Draft Whole document N Greenwood E Johnston compilation 07/08/2020 T Barnfield; V.1.1 Draft Whole document N Greenwood E Johnston Internal QA 18/08/2020 T Barnfield; V.1.2 Draft Whole document A Doyle E Johnston JNCC QA 25/08/2020 T Barnfield; V1.3 Draft Whole Document G7 Leanne E Johnston QA Stockdale 25/08/2020 T Barnfield; V1.4 Draft Update following G7 Leanne E Johnston QA Stockdale 25/01/2021 T Barnfield; V2.0 – 2.4 Draft Updates following NGreenwood; K Saunders; new data availability J Duffill Telsnig T Dixon; E and QA Siegal 01/02/2021 T Barnfield; V2.5 Final Finalise comments Nick Greenwood K Saunders; E and updates Siegal 1 Dogger Bank Special Area of Conservation (SAC) MMO Fisheries Assessment 2020 Contents Document Control ........................................................................................................... -
Appendix 13.2 Marine Ecology and Biodiversity Baseline Conditions
THE LONDON RESORT PRELIMINARY ENVIRONMENTAL INFORMATION REPORT Appendix 13.2 Marine Ecology and Biodiversity Baseline Conditions WATER QUALITY 13.2.1. The principal water quality data sources that have been used to inform this study are: • Environment Agency (EA) WFD classification status and reporting (e.g. EA 2015); and • EA long-term water quality monitoring data for the tidal Thames. Environment Agency WFD Classification Status 13.2.2. The tidal River Thames is divided into three transitional water bodies as part of the Thames River Basin Management Plan (EA 2015) (Thames Upper [ID GB530603911403], Thames Middle [ID GB53060391140] and Thames Lower [ID GB530603911401]. Each of these waterbodies are classified as heavily modified waterbodies (HMWBs). The most recent EA assessment carried out in 2016, confirms that all three of these water bodies are classified as being at Moderate ecological potential (EA 2018). 13.2.3. The Thames Estuary at the London Resort Project Site is located within the Thames Middle Transitional water body, which is a heavily modified water body on account of the following designated uses (Cycle 2 2015-2021): • Coastal protection; • Flood protection; and • Navigation. 13.2.4. The downstream extent of the Thames Middle transitional water body is located approximately 12 km downstream of the Kent Project Site and 8 km downstream of the Essex Project Site near Lower Hope Point. Downstream of this location is the Thames Lower water body which extends to the outer Thames Estuary. 13.2.5. A summary of the current Thames Middle water body WFD status is presented in Table A13.2.1, together with those supporting elements that do not currently meet at least Good status and their associated objectives.