Commission Implementing Decision of 11 December 2013 confirming measures proposed by the United Kingdom for the protection of marine ecosystems in the areas of conservation Haisborough Hammond & Winterton; Start Point to Plymouth Sound & Eddystone, and Land's End & Cape Bank (notified under document C(2013) 9003) (Only the Dutch, English and French texts are authentic) (2014/13/EU)
EU Decision 2014/13 · Adopted 11 December 2013 · Extends to United Kingdom
Commission Implementing Decision
of 11 December 2013
confirming measures proposed by the United Kingdom for the protection of marine ecosystems in the areas of conservation Haisborough Hammond & Winterton; Start Point to Plymouth Sound & Eddystone, and Land's End & Cape Bank
(notified under document C(2013) 9003)
(Only the Dutch, English and French texts are authentic)
(2014/13/EU)
THE EUROPEAN COMMISSION,
Having regard to the Treaty on the Functioning of the European Union,
Having regard to Council Regulation (EC) No 2371/2002 of 20 December 2002 on the conservation and sustainable exploitation of fisheries resources under the common fisheries policyf1, and in particular Article 9 in conjunction with Article 8(3) thereof,
Whereas:
(1)
Council Directive 92/43/EEC of 21 May 1992 on the conservation of natural habitats and of wild fauna and floraf2 provides for the possibility to designate at EU level specific conservation sites. Under Articles 3 and 4, that Directive requires Member States to establish special areas of conservation and, under Article 6 thereof, to take the necessary measures to protect these sites from disturbance and deterioration.
(2)
By Commission Implementing Decision 2012/13/EUf3 the areas called Haisborough, Hammond & Winterton (UK0030369), Start Point to Plymouth Sound & Eddystone (UK0030373) and Land's End & Cape Bank (UK0030375) were included in the list of Sites of Community Importance under Article 4(2) of Directive 92/43/EEC.
(3)
Measures concerning the conservation, management and exploitation of living aquatic resources are subject to the rules of the common fisheries policy.
(4)
Article 9 of Regulation (EC) No 2371/2002 enables Member States to take non-discriminatory measures to minimise the effect of fishing on the conservation of marine ecosystems within 12 nautical miles, provided that the Union has not adopted measures addressing conservation or management specifically for that area. Directive 92/43/EEC requires the establishment of conservation measures as necessary for these sites. The Member States’ measures must be compatible with the objectives of the common fisheries policy as set out in Article 2 of Regulation (EC) No 2371/2002 and no less stringent than existing Union legislation. If the measures apply to fishing vessels from other Member States, they must be notified to the Commission, to the Member States and to the Regional Advisory Councils concerned and be subsequently confirmed by the Commission.
(5)
On 18 November 2013 the United Kingdom notified the measures it intends to take in the above three areas of conservation to Belgium and France, which are the Member States concerned by the measures, as well as to the North Sea Regional Advisory Council, the North Western Waters Regional Advisory Council and to the European Commission.
(6)
The measures put forward on the basis of Directive 92/43/EEC by the United Kingdom establish a zoning of the three areas of conservation, and the prohibition to use any bottom towed fishing gear within specified areas in each of the three designated areas of conservation. For the purposes of the measures addressed by this Decision, the United Kingdom defines bottom towed gear as any fishing gear pushed or pulled through the water which touches the seabed. This includes demersal otter trawls, demersal beam trawls and towed and suction dredges.
(7)
The measures proposed by the United Kingdom aim to contribute to the implementation of Directive 92/43/EEC and are compatible with the objectives set out in Article 2 of Regulation (EC) No 2371/2002, in particular with the precautionary approach to be followed in taking measures designed to protect and conserve living aquatic resources.
HAS ADOPTED THIS DECISION:
Annotations to the whole text
Footnotes
Contents
- 1Article 1
- 2Article 2
- Signature
- Annex EXPLANATORY MEMORANDUM ON THE NOTIFICATION OF THREE BYELAWS TO PROHIBIT BOTTOM TOWED FISHING GEAR IN SPECIFIED AREAS IN UK TERRITORIAL WATERS
- 1INTRODUCTION
- EU LEGAL FRAMEWORK
- 2.1Article 9 of Reg. 2371/2002 (Common Fisheries Policy Basic Regulation)
- 2.2Access to UK territorial waters
- ENGLISH LEGAL FRAMEWORK
- 3.1Marine and Coastal Access Act 2009 (MaCCA)
- 3.2Conservation of Habitats and Species Regulations 2010 (Habitats Regulations)
- 4THE REVISED APPROACH TO MANAGEMENT OF COMMERCIAL FISHERIES IN EUROPEAN MARINE SITES (NATURA 2000 SITES)
- 5PROPOSED MEASURES
- 6ENFORCEMENT OF MEASURES
- 7CONSULTATION OF RELEVANT MEMBER STATES, REGIONAL ADVISORY COUNCILS, AND THE EUROPEAN COMMISSION
- 7.1Consultation dates
- 7.2Responses to public consultation and MMO replies
- 7.3Correspondence between the UK and the European Commission
- ANNEX I
- THE LANDS END AND CAPE BANK EUROPEAN MARINE SITE (SPECIFIED AREA) BOTTOM TOWED FISHING GEAR BYELAW
- Interpretation
- 1Division 1
- Prohibition
- 2Division 2
- Exemption for Scientific, Stocking or Breeding Purposes
- 3Division 3
- Citation
- 4Division 4
- Ls
- EDULEDefinition of Cape Bank
- Explanatory Note
- Division
- Division
- Division
- Division
- ANNEX II
- THE START POINT TO PLYMOUTH SOUND AND EDDYSTONE EUROPEAN MARINE SITE (SPECIFIED AREAS) BOTTOM TOWED FISHING GEAR BYELAW
- Interpretation
- 1In this byelaw:
- Prohibition
- 2Division 2
- Exemption for Scientific, Stocking or Breeding Purposes
- 3Division 3
- Citation
- 4Division 4
- Ls
- EDULEDefinitions of Hatt Rock and Brentons
- Explanatory Note
- Division
- Division
- Division
- Division
- ANNEX III
- THE HAISBOROUGH HAMMOND AND WINTERTON EUROPEAN MARINE SITE (SPECIFIED AREAS) BOTTOM TOWED FISHING GEAR BYELAW
- Interpretation
- 1Division 1
- Prohibition
- 2Division 2
- Exemption for Scientific, Stocking or Breeding Purposes
- 3Division 3
- Citation
- 4Division 4
- Ls
- EDULEDefinitions of Area 1 and Area 2
- Explanatory Note
- Division
- Division
- Division
- Division
- ANNEX IV
- EVIDENCE BASE
- Introduction
- 1.1Division 1.1
- 1.2Division 1.2
- 1.3Division 1.3
- 1.4Division 1.4
- 1.5Division 1.5
- 1.6Division 1.6
- 1.7Division 1.7
- 1.8Division 1.8
- Rationale for intervention
- 2.1Division 2.1
- 2.2Division 2.2
- 2.3Paragraphs 6(1) and 6(2) of the Habitats Directive require that, within special areas of conservation (SACs) and special protection areas (SPAs), member states shall:
- 2.4Division 2.4
- 2.5Division 2.5
- 2.6Division 2.6
- 2.7Division 2.7
- 2.8Division 2.8
- 2.9Market failures occur when market does not deliver an efficient outcome. In the context of the marine environment these failures can be described as:
- 2.10Division 2.10
- Policy objectives and intended effects
- 3.1Division 3.1
- 3.2Division 3.2
- 3.3The conservation objectives of this site are:
- 3.4Division 3.4
- The options
- 4.1Division 4.1
- 4.1.1Option 1: Do nothing
- 4.1.2Option 2: Voluntary agreement
- 4.1.3Option 3: MMO byelaw prohibiting bottom towed gear throughout the SCI (‘full site closure’)
- 4.1.4Option 4: MMO byelaw to prohibit bottom towed gears over Sabellaria spinulosa reef features with appropriate buffering (‘zoned management’).
- 4.1.5Management of activity through a statutory instrument, regulating order or fishing licence condition
- Recommended Option:
- 4.2.1Division 4.2.1
- 4.2.2Division 4.2.2
- Evidence base
- 5.1Division 5.1
- 5.2Bedrock reef feature distribution
- Sectors affected
- 6.1Division 6.1
- 6.2Division 6.2
- 6.3Division 6.3
- Analysis of costs and benefits
- Costs for recommended option
- 7.1.1Division 7.1.1
- 7.1.2Division 7.1.2
- Analysis of fisheries costs
- 7.2.1Division 7.2.1
- 7.3Uncertainty and data assumptions
- 7.3.1Division 7.3.1
- 7.3.2Division 7.3.2
- 7.3.3Division 7.3.3
- 7.3.4Division 7.3.4
- 7.4Fishing activities within Land’s End and Cape Bank SCI
- 7.4.1Division 7.4.1
- 7.4.2Division 7.4.2
- 7.4.3Division 7.4.3
- 7.4.4Division 7.4.4
- 7.4.5Division 7.4.5
- 7.4.6Division 7.4.6
- Valuation of affected landings
- United Kingdom
- 7.5.1Division 7.5.1
- 7.5.2Division 7.5.2
- 7.5.3Division 7.5.3
- 7.5.4Division 7.5.4
- 7.5.5Division 7.5.5
- France and Belgium
- 7.5.6Division 7.5.6
- 7.5.7Division 7.5.7
- 7.5.8Division 7.5.8
- Likely effects on fishing fleet from closure
- 7.6.1Division 7.6.1
- Adaptability
- 7.7.1Division 7.7.1
- 7.7.2Division 7.7.2
- 7.7.3Division 7.7.3
- 7.7.4Division 7.7.4
- Indirect costs
- 7.8.1Environmental costs
- Administrative and enforcement costs
- 7.9.1Division 7.9.1
- 7.9.2Division 7.9.2
- Benefits of recommended option
- 7.10.1Division 7.10.1
- Environmental benefits
- 7.11.1Division 7.11.1
- 7.11.2Division 7.11.2
- 7.11.3Division 7.11.3
- 7.11.4Division 7.11.4
- 7.11.5Division 7.11.5
- 7.11.6Division 7.11.6
- Socio-economic benefits
- 7.12.1Division 7.12.1
- 7.12.2Division 7.12.2
- Distribution of costs and benefits
- 7.13.1Division 7.13.1
- Annex A: Notes of UK fishery statistics data extraction and tables
- Annex B: Notes of Non-UK fishery statistics data
- ANALYSIS OF NON-UK VESSEL VMS ACTIVITY IN ICES RECTANGLES COVERING THE SCI RELATING TO THIS IMPACT ASSESMENT
- Methodology used:
- SUMMARY OF ACTIVITY BY BELGIAN AND FRENCH VESSELS IN ICES RECTANGLE 29E4 COVERING THE LANDS END AND CAPE BANK SITE
- ANNEX V
- EVIDENCE BASE
- Introduction
- 1.1Division 1.1
- 1.2Division 1.2
- 1.3Division 1.3
- 1.4Division 1.4
- 1.5Division 1.5
- 1.6Division 1.6
- 1.7Division 1.7
- 1.8Division 1.8
- Rationale for intervention
- 2.1Division 2.1
- 2.2Division 2.2
- 2.3Paragraphs 6(1) and 6(2) of the Habitats Directive require that, within special areas of conservation (SACs) and special protection areas (SPAs), member states shall:
- 2.4Division 2.4
- 2.5Division 2.5
- 2.6Division 2.6
- 2.7Division 2.7
- 2.8Division 2.8
- 2.9Market failures occur when the market does not deliver an efficient outcome. In the context of the marine environment these failures can be described as:
- 2.10Division 2.10
- Policy objectives and intended effects
- 3.1Division 3.1
- 3.2Division 3.2
- 3.3The conservation objectives of this site are:
- 3.4Division 3.4
- The options
- 4.1Division 4.1
- 4.1.1Option 1: Do nothing
- 4.1.2Option 2: Voluntary agreement
- 4.1.3Option 3: MMO byelaw prohibiting bottom towed gear throughout the SCI (‘full site closure’)
- 4.1.4Option 4: MMO byelaw to prohibit bottom towed gears over Sabellaria spinulosa reef features with appropriate buffering (‘zoned management’).
- 4.1.5Option 5: Management of activity through a statutory instrument, regulating order or fishing licence condition
- Recommended Option:
- 4.2.1Division 4.2.1
- 4.2.2Division 4.2.2
- Evidence Base
- Impacts of bottom towed gear activity on bedrock reef
- 5.1.1Division 5.1.1
- 5.2Bedrock reef feature distribution
- Sectors affected
- 6.1Division 6.1
- 6.2Division 6.2
- 6.3Division 6.3
- Analysis of costs and benefits
- Costs for recommended option
- 7.1.1Division 7.1.1
- 7.1.2Division 7.1.2
- Analysis of fisheries costs
- 7.2.1Division 7.2.1
- Uncertainty and data assumptions
- 7.3.1Division 7.3.1
- 7.3.2Division 7.3.2
- 7.3.3Division 7.3.3
- 7.3.4Division 7.3.4
- 7.4Fishing activities within Start Point to Plymouth Sound and Eddystone SCI
- 7.4.1Division 7.4.1
- 7.4.2Division 7.4.2
- 7.4.3Division 7.4.3
- 7.4.4Division 7.4.4
- 7.4.5Division 7.4.5
- 7.4.6Division 7.4.6
- 7.4.7Division 7.4.7
- Valuation of affected landings
- United Kingdom
- 7.5.1Division 7.5.1
- 7.5.2Division 7.5.2
- 7.5.3Division 7.5.3
- 7.5.4Division 7.5.4
- 7.5.5Division 7.5.5
- France and Belgium
- 7.5.6Division 7.5.6
- 7.5.7Division 7.5.7
- Likely effects on fishing fleet from closure
- 7.6.1Division 7.6.1
- Adaptability
- 7.7.1Division 7.7.1
- 7.7.2Division 7.7.2
- 7.7.3Division 7.7.3
- 7.7.4Division 7.7.4
- Indirect costs
- Environmental costs
- 7.8.2Division 7.8.2
- 7.8.3Division 7.8.3
- Administrative and enforcement costs
- 7.9.1Division 7.9.1
- 7.9.2Division 7.9.2
- Benefits of recommended option
- 7.10.1Division 7.10.1
- Environmental benefits
- 7.11.1Division 7.11.1
- 7.11.2Division 7.11.2
- 7.11.3Division 7.11.3
- 7.11.4Division 7.11.4
- 7.11.5Division 7.11.5
- 7.11.6Division 7.11.6
- Socio-economic benefits
- 7.12.1Division 7.12.1
- 7.12.2Division 7.12.2
- Distribution of costs and benefits
- 7.13.1Division 7.13.1
- Annex A: Notes of UK fishery statistics data extraction and tables
- Annex B: Notes of Non-UK fishery statistics data
- ANALYSIS OF NON-UK VESSEL VMS ACTIVITY IN ICES RECTANGLES COVERING THE SCI RELATING TO THIS IMPACT ASSESMENT
- Methodology used:
- SUMMARY OF ACTIVITY BY BELGIAN AND FRENCH VESSELS IN ICES RECTANGLES 29E5 & 29E6 COVERING PLYMOUTH SOUND, START POINT AND EDDYSTONE SITE
- ANNEX VI
- EVIDENCE BASE
- Introduction
- 1.1Division 1.1
- 1.2Division 1.2
- 1.3Division 1.3
- 1.4Division 1.4
- 1.5Division 1.5
- 1.6Division 1.6
- 1.7Division 1.7
- Rationale for intervention
- 2.1Division 2.1
- 2.2Division 2.2
- 2.3Paragraphs 6(1) and 6(2) of the Habitats Directive require that, within special areas of conservation (SACs) and special protection areas (SPAs), member states:
- 2.4Division 2.4
- 2.5Division 2.5
- 2.6Division 2.6
- 2.7Division 2.7
- 2.8Division 2.8
- 2.9Market failures occur when the market does not deliver an efficient outcome. In the context of the marine environment these failures can be described as:
- 2.10Division 2.10
- Policy objectives and intended effects
- 3.1Division 3.1
- 3.2Division 3.2
- 3.3The conservation objectives of this site are:
- 3.4Division 3.4
- The options
- 4.1Division 4.1
- 4.1.1Option 1: Do nothing
- 4.1.2Option 2: Voluntary agreement
- 4.1.3Option 3: MMO byelaw prohibiting bottom towed gear throughout the SCI (‘full site closure’)
- 4.1.4Option 4: MMO byelaw to prohibit bottom towed gears over Sabellaria spinulosa reef features with appropriate buffering (‘zoned management’).
- 4.1.5Management of activity through a statutory instrument, regulating order or fishing licence condition
- Recommended option:
- 4.2.1Division 4.2.1
- 4.2.2Division 4.2.2
- Evidence Base
- 5.1Impacts of bottom towed gear activity on Sabellaria spinulosa reef:
- 5.2Reef distribution
- Sectors affected
- 6.1Division 6.1
- 6.2Division 6.2
- 6.3Division 6.3
- Analysis of costs and benefits
- Costs for recommended option
- 7.1.1Division 7.1.1
- 7.1.2Division 7.1.2
- Analysis of fisheries costs
- 7.2.1Division 7.2.1
- Uncertainty and data assumptions
- 7.3.1Division 7.3.1
- 7.3.2Division 7.3.2
- 7.3.3Division 7.3.3
- 7.3.4Division 7.3.4
- 7.4Fishing activities within Haisborough, Hammond and Winterton SCI
- 7.4.1Division 7.4.1
- 7.4.2Division 7.4.2
- 7.4.3Division 7.4.3
- 7.4.4Division 7.4.4
- 7.4.5Division 7.4.5
- 7.4.6Division 7.4.6
- 7.4.7Division 7.4.7
- Valuation of affected landings
- United Kingdom
- 7.5.1Division 7.5.1
- 7.5.2Division 7.5.2
- 7.5.3Division 7.5.3
- 7.5.4Division 7.5.4
- 7.5.5Division 7.5.5
- Belgium
- 7.5.6Division 7.5.6
- 7.5.7Division 7.5.7
- 7.5.8Division 7.5.8
- Likely effects on fishing fleet from closure
- 7.6.1Division 7.6.1
- 7.6.2Division 7.6.2
- Adaptability
- 7.7.1Division 7.7.1
- 7.7.2Division 7.7.2
- 7.7.3Division 7.7.3
- 7.7.4Division 7.7.4
- Indirect costs
- Environmental costs
- 7.8.2Division 7.8.2
- 7.8.3Division 7.8.3
- Administrative and enforcement costs
- 7.9.1Division 7.9.1
- 7.9.2Division 7.9.2
- Benefits of recommended option
- 7.10.1Division 7.10.1
- Environmental benefits
- 7.11.1Division 7.11.1
- 7.11.2Division 7.11.2
- 7.11.3Division 7.11.3
- 7.11.4Division 7.11.4
- 7.11.5Division 7.11.5
- Socio-economic benefits
- 7.12.1Division 7.12.1
- 7.12.2Division 7.12.2
- Distribution of costs and benefits
- 7.13.1Division 7.13.1
- Annex A: Notes of fishery statistics data extraction and tables
- Annex B: Notes of Non-UK fishery statistics data
- ANALYSIS OF NON-UK VESSEL VMS ACTIVITY IN ICES RECTANGLES COVERING THE SCI RELATING TO THIS IMPACT ASSESMENT
- Methodology used:
- SUMMARY OF ACTIVITY BY BELGIAN VESSELS IN ICES RECTANGLES COVERING HAISBOROUGH HAMMOND AND WINTERTON SITE