Of Herring Larvae in the Northern North Sea, Changes in Recent Years

Total Page:16

File Type:pdf, Size:1020Kb

Of Herring Larvae in the Northern North Sea, Changes in Recent Years THE DISTRIBUTION AND ABUNDANCE OF HERRING LARVAE IN THE NORTHERN NORTH SEA, CHANGES IN RECENT YEARS By A. S a v il l e Marine Laboratory, Aberdeen, Scotland ln 1951 the Marine Laboratory, Aberdeen, began a water column through which the sampler fished. For regular programme to investigate the distribution and the earlier material, taken with a 1 metre silk net, the abundance of autumn spawned herring larvae in the sample numbers were also converted to this basis using north-western North Sea. It was decided to sample the the conversion factors from 1 metre to Gulf III calcu­ area from 56°00' N to 59°45' N and from the Scottish lated from the large number of paired hauls made coast to the prime meridian as this would cover all of with the two gears in 1957. the known major spawning areas within Scottish The numbers of larvae in the sampled area on each waters (W o od 1930, C la rk 1933). This programme cruise were calculated by contouring at levels of 1, 5, has been carried out every year from 1951 to 1967 10, 50, 250 and 1 000 larvae per square metre, meas­ with the exception of 1956. Due to interruptions by uring the area in square metres within each contour, bad weather and by ships defects the intensity of raising these areas by the appropriate contour level and sampling and the proportion of the total area sampled summing the values so obtained. has varied somewhat from year to year. Part of the In the area under consideration hatching of herring material has already been presented in a paper to the larvae begins about the middle of August and continues Pelagic Fish (Northern) Committee of ICES. (Saville, to the middle of October. In those years when several 1966). Since then additional material has been col­ cruises were completed during this period the curve of lected and analysed which throws some new light on larval abundance against time strongly suggests that the matter and the subject is of sufficient importance the preponderance of hatching takes place in Septem­ to the objectives of this symposium for its re-presen­ ber. In all years the highest abundance of larvae in the tation to demand little in the way of apologies. 10-15 mm size range has also been found in Septem­ ber. As this is the month in which the area was best sampled, in this paper consideration of the abundance METHODS and distribution of larvae is confined to the cruises From 1951 until 1957 sampling was done by timed which took place in that month. oblique hauls from bottom to surface with a 1 metre The distributions of larvae in the smallest size cate­ net of bolting silk with 60 threads per inch. In 1957 gory suggest that the area sampled can be divided the modified Gulf III sampler (B r i d g e r , 1958), now into two clearly demarcated areas of larval production, widely accepted as the standard sampling instrument the Buchan area to the south of 57°40'N, and em­ for herring larvae by European workers, was intro­ bracing the well known herring spawning grounds of duced. In that year, so as to give a basis for com­ Turbot Bank, and Aberdeen Bank; and what will be parison with earlier material, at each station on all termed the Shetland area to the north of 57°40' N cruises a sample was taken with both the Gulf III and including the Clythness spawning ground and the and the 1 metre oblique net. spawning grounds around Orkney. In the 10-15 mm Larvae caught on these surveys were grouped into size group the two distributions are not so clearly three size intervals less than 10 mm, 10-15 mm, and separated, and in larger larvae than this they merge over 15 mm. Only the first two of these size groups completely, but for the 10-15 mm sizes they are still will be considered here as providing information on sufficiently distinct for it to be convenient to retain variations in the size of the spawning stock and its this subdivision. distribution at spawning. For Gulf III hauls the num­ Material is available from sampling in September bers in a size group were converted to the number for all years since 1951, except for 1956 in the Buchan below a square metre of surface from the volume of area, and for all years except 1956 and 1957 in the water filtered at that station, as measured by a Currie- Shetland area. In most years, at least two surveys of Foxton or T.S.K. flowmeter, and the depth of the the area were done in this month. 88 A. Saville 1000/m2 250/m2 Figure 35. Distribution of larvae less than 10 mm in September Figure 36. Distribution of larvae less than 10 mm in September 1951-54. 1955-1960. DISTRIBUTION OF LARVAE Unfortunately it is not possible, in the space avail­ 60° able, to provide charts of the distribution of the larvae on all the cruises over the years 1951-1966. It has been decided to illustrate only the distributions of the smallest size group as providing the best index of the centres of, and changes in, the spawning sites. The 10-15 mm size category in any case, although showing 59* greater dispersion, normally have a very similar distri­ bution of the areas of greatest density to those of the larvae less than 10 mm. In Figures 35—37 are shown the generalised distributions of larvae less than 10 mm b 0 in three time periods, 1951-54, 1955-60, and 1961-66. 58° These were chosen as being periods within which the distributions did not change appreciably but between which there were quite marked changes. The contour levels of 1 000 and 250 larvae per square metre only 1000/m 2 are illustrated as giving the best index of major spawning in these years. 57* 250/m2 In Figure 35 are shown the areas within which more than 1 000 and more than 250 recently hatched larvae were taken below 1 square metre of surface in 1951- 54. It will be seen that at this time larvae were not very plentiful in the northern area. No concentrations 56" of larvae exceeding 1 000 per square metre were de­ tected around Orkney but there was a band of larvae at 250 per square metre to the north and east of the Figure 37. Distribution of larvae less than 10 mm in September islands. In the Buchan area a small patch of larvae at 1961-1966. Herring larvae in the northern North Sea 89 concentrations of 1 000 per square metre was located However, in the period 1957-63 the area was well close to the Aberdeenshire coast while a considerably sampled and the abundances of this size group in the larger patch of the same density was found over Turbot Buchan area were fairly constant at a level appreciably Bank and Aberdeen Bank. In the period 1955-60 (Fig. lower than in 1951-54. In 1964, as mentioned above, 36) larvae of this size group were more abundant there was a build up in abundance in the Buchan area in the Orkney area with a concentration of larvae to around the level found in the earlier period. In exceeding 1 000 per square metre of the east of the 1965, 1966 and 1967 there was a further sharp pro­ islands, enclosed by a large area containing more than gressive fall in this size category in the Buchan area to 250 larvae per square metre. In the Buchan area during an extremely low level. this period the patch of high density of larvae close to In the Shetland area (Fig. 39) the abundance of the the Aberdeenshire coast was not in evidence and only size group less than 10 mm has fluctuated more widely two small areas of larvae of more than 1,000 per square from year to year but in seems clear that in this area metre were found on Aberdeen Bank and to the east they were considerably less numerous on average in the of Montrose Bank. years up to and including 1955 than they have been In the period 1961-66, as shown in Figure 37, in the years sampled since then. this situation has developed still further with a marked When considering the size of the spawning stock in increase in the abundance of larvae of this size group the north-western North Sea the total production of around Orkney and off Clythness. In the Buchan area larvae within the area is of greater relevance. In during this period the distribution of larvae of this Figure 40 is shown a measure of this obtained by size category has been much more variable. From 1951 summing the mean September abundances for the to 1963 their distributional pattern has been very close Buchan and Shetland areas. Although there are major to that shown in Figure 37 with no concentrations variations from year to year there is little evidence exceeding 1 000 per square metre in the Turbot and here of any long-term trend of declining larval pro­ Aberdeen Bank area and the area enclosed by the duction over the area as a whole such as has been 250 per square metre contour diminishing still further. In these years, however, there has been evidence of 22 -, high concentrations of larvae in the area of Berwick East Bank which was not apparent in the earlier 2 0 - periods.
Recommended publications
  • General Orkney Fisheries Association Represents 51 Vessel Owners and 2
    General Orkney Fisheries Association represents 51 vessel owners and 2 Shellfish processors . The Association is tasked with protecting the interests of its members and the wider industry as it impacts on our members. OFA welcome the opportunity to respond to the Consultation on prospective Marine Protected Areas. OFA have been involved in the series of workshops instigated by Marine Scotland in the gestation of the pMPA process. OFA must reflect the view of its members that the p MPA designations are not viewed with simple acceptance by fishermen as a development that will benefit them, but have been willing throughout the process to adopt the view that if pMPAs do not restrict current fishing then it would not be reasonable to oppose them per se. OFA find the position complex as in some respects and through pursuit of their own interests, it may mean that designation might limit their direct competitors, however it may also open up unwanted potential for future unwanted restrictions on themselves. Notwithstanding the above OFA members are deeply sceptical given the history of land designations for SPAs and SSSIs which have resulted in the unscientific development of management measures often via the single interest objectives of NGOs which have resulted in the misalignment of species to the detriment of other species and limited the economic viability of legitimate human economic activity. We cite the increase in the Skua population in Hoy Orkney as an instance of management that has caused the predatory depletion of smaller birds as well as restrictions on animal grazing which has similarly caused unforeseen consequences in the available food sources to other species.
    [Show full text]
  • Variability of UK Marine Resources
    Variability of UK marine resources An assessment of the variability characteristics of the UK’s wave and tidal current power resources and their implications for large scale development scenarios Commissioned by The Carbon Trust Produced by the Environmental Change Institute July 2005 This report has been prepared by the Environmental Change Institute solely for use by the Carbon Trust by whom it was commissioned. It is not addressed to and may not be relied upon by any person or entity other than the Carbon Trust without the prior written permission of both the Carbon Trust and the Environmental Change Institute. In producing this report, the Environmental Change Institute has relied upon information provided by third parties. Neither the Carbon Trust nor the Environmental Change Institute nor their respective directors, employees or affiliated companies give any representation or warranty, express or implied, as to the accuracy, completeness or fairness of the contents of the report, nor accept any responsibility or liability for any loss, whether direct, indirect or consequential, arising from reliance on it. Any use of this report by any third party for whatever purpose is solely the responsibility of that party who should use such due diligence to verify the report's contents and consult its own advisers as may be appropriate. The Carbon Trust does not give investment advice and nothing in this report constitutes, or should be taken as, a recommendation to enter into, or the giving of any advice in relation to, any investment. This report may be copied and distributed only with the consent of the Carbon Trust.
    [Show full text]
  • Marine Protected Areas and Large-Scale Features. Position Paper
    Marine Protected Areas and Large-Scale Features. Position paper Summary This document considers the role of large-scale features in developing the Marine Protected Area (MPA) network in Scotland’s seas. It describes each of the large-scale features, outlines the approach to their inclusion in the process, and considers the possible MPAs and MPA search locations which contain these features in relation to the evidence available. Five large-scale features are included on the list of MPA search features: seamounts; continental slope; shelf deeps; shelf banks and mounds; and fronts. These features have been included to represent areas of potential wider significance to the overall health and biodiversity of Scotland’s seas in the development of the MPA network. Specific examples of large-scale features have only been included in possible MPAs and MPA search locations where evidence is available to suggest that they contribute to ecosystem function, for instance in terms of playing a key supporting role within the site or more widely; or providing functional links within the site; or in supporting linkages within the network and wider seas. It is anticipated that MPAs may be able to provide direct protection for large-scale features through management of pressures that have implications for their extent, structure and distribution within the site and thereby their wider function. Draft conservation objectives are to ‘conserve’ the function of large scale features included as protected features. In total 13 areas (10 possible MPAs and 3 MPA search locations) have been identified for large-scale features, where evidence is available to suggest they play a role in supporting ecological function.
    [Show full text]
  • Offshore Seabed Survey of Turbot Bank Possible MPA
    JNCC/Cefas Partnership Report Series Report No. 20 Offshore seabed survey of Turbot Bank possible MPA Eggleton, J., Diesing, M. & Schinaia, S. July 2019 © JNCC, Cefas 2019 ISSN 2051-6711 Offshore seabed survey of Turbot Bank possible MPA Eggleton, J., Diesing, M. & Schinaia, S. Report completed 2013 and published July 2019 © JNCC, Cefas, 2019 ISSN 2051-6711 For further information, please contact: Joint Nature Conservation Committee Monkstone House City Road Peterborough PE1 1JY http://jncc.defra.gov.uk This report is compliant with the JNCC Evidence Quality Assurance Policy http://jncc.defra.gov.uk/default.aspx?page=6675 and has been reviewed by Cefas and JNCC prior to publication. This report should be cited as: Eggleton, J., Diesing, M. & Schinaia, S. 2019. Offshore seabed survey of Turbot Bank possible MPA. JNCC/Cefas Partnership Report No. 20. JNCC, Peterborough, ISSN 2051- 6711. Summary This report presents the findings from analyses of the acoustic data and groundtruth samples gathered during the seabed survey of the Turbot Bank possible Marine Protected Area (pMPA). Turbot Bank lies within a coarse sandy sediment plain to the east of Scotland, approximately 65km east of Peterhead on the Aberdeenshire coast, south of the Fladen Ground, and comprises a shelf bank and mound feature. The report describes the presence, location and extent of broadscale habitats, biotopes and Scottish Marine Protected Area (SMPA) Priority Marine Features within the Turbot Bank pMPA. Full coverage multibeam echosounder data (bathymetry and backscatter) collected under the Civil Hydrography Programme were available for the western half of Turbot Bank pMPA. During a dedicated survey in December 2012, new acoustic data were collected in the eastern part of the bank.
    [Show full text]
  • Association of Salmon Fishery Boards Comments on the Consultation on Possible Nature Conservation Marine Protected Areas November 2013
    Association of Salmon Fishery Boards Comments on the Consultation on Possible Nature Conservation Marine Protected Areas November 2013 Introduction The Association of Salmon Fishery Boards is the representative body for Scotland's 41 District Salmon Fishery Boards (DSFBs) including the River Tweed Commission (RTC), which have a statutory responsibility to protect and improve salmon and sea trout fisheries. The Association and Boards work to create the environment in which sustainable fisheries for salmon and sea trout can be enjoyed. Conservation of fish stocks, and the habitats on which they depend, is essential and many DSFB’s operate riparian habitat enhancement schemes and have voluntarily adopted ‘catch and release’ practices, which in some cases are made mandatory by the introduction of Salmon Conservation Regulations. ASFB creates policies that seek where possible to protect wider biodiversity and our environment as well as enhancing the economic benefits for our rural economy that result from angling. An analysis completed in 2004 demonstrated that freshwater angling in Scotland results in the Scottish economy producing over £100 million worth of annual output, which supports around 2,800 jobs and generates nearly £50million in wages and self-employment into Scottish households, most of which are in rural areas. General comments We welcome the opportunity to comment on this consultation. ASFB believe that an ecologically coherent network of Marine Protected Areas with an aim of protecting and enhancing Scotland’s marine environment is extremely important. Whilst we recognise that none of the proposed MPAs will be specifically designated for Atlantic salmon or sea trout, we believe that there will be additional benefits to these species during the marine phase of their life cycle.
    [Show full text]
  • Coastlines Are Reproduced Using GEBCO Digital Atlas, Centenary Edition 2003
    Subsea Cables UK is an industry organisation with the aim of promoting marine safety, safeguarding submarine cables and encouraging excellent practice within the industry. Subsea Cables UK does not broadly differentiate between the Communications, Power and Renewable industry cables as their impact on other seabed stakeholders is so similar. Subsea Cables UK is interested in any cables which land or pass through UK waters including the Exclusive Economic Zone. SOUTH WEST APPROACHES Kingfisher Awareness Chart Kilmore! New Quay! 13°W 30' 12°W 30' 11°W 30' 10°W 30' IRELAN9D°! W 30' 8°W 30' 7°W 30' 6°W 30' 5°W 30' 4°W 30' 3°W C U ! E K L - T I ! I R 52°N C 52°N E Fishguard ( L O A Cork O N REPUBLIC OF IRELAND ! S D ) Saltees Ground + C ! 4 R St. David's 4 O ( 0 S ) S ¥ 8 WALES 4 I ! 5 N 7 G 5 5 2 5 9 + 9 4 Kinsale 9 4 Milford! Haven ! ( 0 ) 2 0 8 Swansea 5 ! Ballycotton Ground 1 Dursey Island ! 0 Turbot Bank 3 1 Our aim is to optimise coexistence and minimise any hazards 1 Oxwich 9 ! P NYMPHE 0 T 520 + A 7 674 30' 4 T 0)20 ! 30' 4 +44( ( IR S Cardiff 0 OLA ) I S 2 S Marine Safety 0 H 7 B Kinsale Head Grounds 6 R S 7 W 4 A BANK 5 N AN 2 C S 0 H E 0 00 The Smalls Ground A/ 452 BR 7 67 EA (0)20 N +4 +44 4(0 ) 0 g 2 207 67452 0 H Se 5200 RT 674 U + O 7 K I N )20 AL (0 G 4 - N 44 U I I + T 4 R M AT OR E T P ( E E P - S K 0 G U L ! E ) P A A O 2 N Lundy Island UR 98 T .E 2 0 6 D W 6 8 A 2 1 T 9 TA 8 C 00 + 5 54 08 R 1 06 0 4 caused by the installation or presence of submarine cables to other sea bed users.
    [Show full text]
  • Planning Scotland's Seas
    Planning Scotland’s Seas 2013 Possible Nature Conservation Marine Protected Areas Consultation Overview Planning Scotland’s Seas 2013 Possible Nature Conservation Marine Protected Areas Consultation Overview The Scottish Government, Edinburgh 2013 © Crown copyright 2013 You may re-use this information (excluding logos and images) free of charge in any format or medium, under the terms of the Open Government Licence. To view this licence, visit http://www.nationalarchives.gov.uk/doc/open-government-licence/ or e-mail: [email protected]. Where we have identified any third party copyright information you will need to obtain permission from the copyright holders concerned. This document is also available from our website at www.scotland.gov.uk. ISBN: 978-1-78256-764-6 The Scottish Government St Andrew’s House Edinburgh EH1 3DG Produced for the Scottish Government by APS Group Scotland DPPAS14502 (07/13) Published by the Scottish Government, July 2013 Ministerial Foreword We are at a monumental point in the history of Scotland‟s seas. This consultation provides everyone with an interest in our marine environment to help us develop a network of Marine Protected Areas to ensure that our marine ecosystems are resilient and can continue to support our society‟s needs for generations to come. At the same time we are also consulting on the draft National Marine Plan, draft sectoral marine plans for offshore renewable energy and priority marine features. Protecting rare, representative and productive species and habitats on the basis of sound science means we can keep on getting these benefits and enjoying the rich diversity of life in the waters around us.
    [Show full text]
  • Marine Scotland Consultations
    ABERDEEN CITY COUNCIL COMMITTEE Enterprise, Strategic Planning & Infrastructure DATE 12 November 2013 DIRECTOR Gordon McIntosh TITLE OF REPORT Marine Scotland Consultations REPORT NUMBER: EPI/13/197 1. PURPOSE OF REPORT The purpose of this report is to present the draft response on behalf of the Council for five Marine Scotland consultations under the heading ‘Planning Scotland’s Seas’. 2. RECOMMENDATION(S) That the committee: - a) Approves the draft consultation response for submission to the Scottish Government. 3. FINANCIAL IMPLICATIONS There are no financial implications identified as a result of this consultation. The Marine (Scotland) Act 2010 states that marine planning functions will be delegated to a regional level via Marine Planning Partnerships (MPP). The MPP should consist of appropriate stakeholders including local authorities. At this level, the National Marine Plan will be implemented locally through a regional marine plan. By this time, there will be a better understanding of potential financial implications to the Council associated with this function. The exact timeframe for implementation is still not known. 4. OTHER IMPLICATIONS The development of a National Marine Plan is a statutory requirement of the Marine (Scotland) Act 2010. Part 3 of the Act places a duty on Scottish Ministers to prepare and adopt a National Marine Plan, followed by regional marine plans. These consultations are some of the steps being taken to meet this requirement. 5. BACKGROUND/MAIN ISSUES The Marine (Scotland) Act 2010 allows for the management of the competing demands on marine resources to be more effective. This ensures that the marine environment is protected and enhanced so that it continues to provide economic and social benefits for future generations.
    [Show full text]
  • SNH Commissioned Report 547: Advice to the Scottish Government on the Selection of Nature Conservation Mpas
    Scottish Natural Heritage Joint Nature Conservation Committee Commissioned Report No. 547 Advice to the Scottish Government on the selection of Nature Conservation Marine Protected Areas (MPAs) for the development of the Scottish MPA network Photography From top left-hand corner working sequentially in rows across the page to bottom right-hand corner – Images 1, 4, 5, 12 and 18 © Paul Kay, Marine Wildlife Photo Agency (http://www.marinewildlife.co.uk) Image 2 © Sue Scott Image 22 © Richard Shucksmith (www.rshucksmith.co.uk) Images 11 and 21 © Paul Naylor (www.marinephoto.co.uk) Images 6, 8, 14 and 25 © Crown copyright, Marine Scotland Image 10 © BIS and JNCC Image 20 © JNCC Images 3, 7, 9, 13, 15, 15, 16, 17, 19, 23 and 24 © SNH ADVICE TO GOVERNMENT Commissioned Report No. 547 Advice to the Scottish Government on the selection of Nature Conservation Marine Protected Areas (MPAs) for the development of the Scottish MPA network For further information on this report please contact: Scottish Natural Heritage Joint Nature Conservation Committee Great Glen House Inverdee House INVERNESS ABERDEEN IV3 8NW AB11 9QA Telephone: 01463 725000 Telephone: 01224 266550 E-mail: [email protected] E-mail: [email protected] This report should be quoted as: Scottish Natural Heritage and the Joint Nature Conservation Committee. (2012). Advice to the Scottish Government on the selection of Nature Conservation Marine Protected Areas (MPAs) for the development of the Scottish MPA network. Scottish Natural Heritage Commissioned Report No. 547 This report, or any part of it, should not be reproduced without the permission of Scottish Natural Heritage or the Joint Nature Conservation Committee.
    [Show full text]
  • Chapter 15: Fish and Shellfish Ecology
    Chapter 15: Fish and Shellfish Ecology NorthConnect KS Phone +47 38 60 70 00 Serviceboks 603, Lundsiden Mail: [email protected] N-4606 Kristiansand Web: www.northconnect.no Norway Chapter 15: Fish and Shellfish Ecology Contents 15 Fish and Shellfish Ecology ...................................................................................................... 15-1 15.1 Introduction ........................................................................................................................... 15-1 15.2 Legislation, Policy and Guidance ............................................................................................ 15-1 15.2.1 Legislative Framework .................................................................................................... 15-1 15.2.2 Policy Framework ............................................................................................................ 15-2 15.2.3 Guidance ......................................................................................................................... 15-3 15.2.4 Consultation .................................................................................................................... 15-3 15.3 Assessment Methodology ...................................................................................................... 15-4 15.3.1 Overview ......................................................................................................................... 15-4 15.3.2 Desk Study ......................................................................................................................
    [Show full text]
  • 29Th Licensing Round – Matrix of Blocks and Conservation Sites – Last Updated 12Th July 2016 the Matrices Included in This D
    29th Licensing Round – Matrix of Blocks and Conservation Sites – Last updated 12th July 2016 The matrices included in this document list blocks in the three 29th seaward licensing round areas (West of Hebrides, East of Shetland and Mid North Sea High) along with their proximity to coastal and offshore conservation sites. The conservation sites include Special Areas of Conservation and Special Protection Areas (SACs and SPAs respectively, collectively termed Natura 2000 sites)1, and Marine Conservation Zones (MCZs) and Marine Protected Areas (MPAs)2. Also listed are the features for which the sites are (or are proposed to be) designated for. The list includes designated sites and those which are at earlier stages in the designation process, including draft and potential sites. Applicants should augment the summary information provided in this document with the most recent site listings on the JNCC website, and also those of the devolved administrations relevant to the 29th Round: Scottish Natural Heritage and the Department of the Environment Northern Ireland. Links to each of the three areas are provided below: West of Hebrides East of Shetland Mid North Sea High 1 made under the Wildlife and Countryside Act 1981 (as amended), the Conservation (Natural Habitats, &c.) Regulations 1994 (as amended), Conservation (Natural Habitats, & c.) Regulations 2010 (as amended) and Offshore Marine Conservation (Natural Habitats & c.) Regulations 2007. 2 made under the Marine and Coastal Access Act 2009 and Marine (Scotland) Act 2010 29th Licensing
    [Show full text]
  • Marine Protected Unprotected Areas
    MARINE PROTECTED UNPROTECTED AREAS A case for a just transition to ban bottom trawl and dredge fishing in offshore Marine Protected Areas Frith Dunkley & Jean-Luc Solandt Ocean Recovery Department Marine Conservation Society, UK [email protected] https://map.mpa-reality-check.org/ Headline figures The study examined fishing effort in all Marine Protected Areas (Special Areas of Conservation, Marine Conservation Zones and nature conservation Marine Protected Areas, hereafter collectively referred to as MPAs) in UK offshore waters (beyond 12 nautical miles) designated to protect the seabed, and the implications for biodiversity recovery and carbon storage. All but one offshore MPA designated to protect the seabed experienced demersal towed fishing between 2015-2018. Half of all offshore MPAs designated to protect the seabed before 2018 have experienced at least 1,000 hours of demersal fishing between 2015 and 2018. 12% of all offshore benthic MPAs designated before 2018 have experienced at least 5,000 hours of demersal fishing between 2015 and 2018. Between 2015 and 2018, the sandbanks and reefs offered “protection” by the UK’s offshore MPAs have experienced at least 89,894 hours of fishing effort by vessels using bottom-contacting mobile gear. The UK fleet was responsible for 43% of demersal fishing recorded inside offshore MPAs between 2015 and 2018 and 63% of the fishing conducted outside these MPAs. The non-UK EU fleet were responsible for 57% of the demersal fishing recorded inside offshore MPAs designated to protect the seabed between 2015 and 20181. The highest fishing rates since site designation were found in Central Fladen ncMPA (northern North Sea in offshore Scottish waters), Margate and Long Sands Special Area of Conservation (SAC) (off the Kent coast) and Haisborough, Hammond and Winterton SAC (off the Norfolk coast) with these sites experiencing fishing across 95-100% of their surface area.
    [Show full text]