Fisheries management measures within Scottish Offshore Marine Protected Areas (MPAs) - Sustainability Appraisal

The Sustainability Appraisal is the overarching document which aims to capture the complexities of the potential socioeconomic and environmental impacts of fisheries management. The Strategic Environmental Assessment and a Socio-Economic Impact Assessment are used the inform the appraisal.


2 Proposals for Fisheries Management Measures

2.1 Designation of the MPA network to date

The Scottish MPA network consists of a large number of sites, designated under various legislative frameworks and includes:

  • Nature Conservation MPAs (NCMPA);
  • Special Areas of Conservation (SACs);
  • Special Protection Areas (SPAs);
  • Sites of Special Scientific Interest (SSSI); and
  • Ramsar sites.

In addition, there is one demonstration and research MPA, eight historic MPAs, and five Other Area Based Measures recognised as part of the Scottish MPA network[10].

Offshore Marine Protected Areas

The Marine and Coastal Access Act 2009[11] gives Scottish Ministers powers to designate MPAs in the Scottish offshore region[12]. To inform this process, the Scottish Nature Conservation MPA Project was established to ensure MPAs are designated in the most appropriate locations for their particular objectives. The Joint Nature Conservation Committee (JNCC) is responsible for providing advice on Nature Conservation MPAs in the offshore environment[13]. There are currently 36 Nature Conservation MPAs located within Scotland’s seas, 13 of which are offshore:[14].

Nature Conservation MPAs help protect rare, representative, and productive benthic species and habitats in Scottish waters, as well as significant geodiversity features[15]. In addition to fulfilling statutory conservation obligations under the Marine and Coastal Access Act 2009, offshore MPAs also form part of the wider OSPAR network of MPAs that are found across the North East Atlantic[16].

Special Areas of Conservation

Scotland currently has 58 SACs with marine components, covering 8% of the Scottish sea area. Nine of these SACs are completely in the Scottish offshore region, and a further two sites have parts in both inshore and offshore waters.

Following the UK leaving the EU, the Conservation (Natural Habitats, &c.) Regulations 1994[17],[18], the Conservation of Habitats and Species Regulations 2017[19], and the Conservation of Offshore Marine Habitats and Species Regulations 2017[20], (collectively known as the Habitats Regulations) have been amended by the Conservation of Habitats and Species (Amendment) (EU Exit) Regulations 2019[21]. These changes ensure that the requirements of the EU Habitats Directive are part of UK domestic legislation, and continue to apply to how SACs are designated and protected[22].

2.2 Requirement for and introduction of management measures

The Marine and Coastal Access Act 2009[23] contains a number of legal provisions which support the protected features of offshore NCMPAs. This includes the need for public authorities to further the achievement of the conservation objectives of Nature Conservation MPAs where possible whilst exercising their own functions. If they cannot further the objectives then they should act in a way that least hinders them. Scottish Ministers have powers under the Marine and Coastal Access Act 2009 to implement orders relating to the exploitation of sea fisheries resources in the Scottish offshore region for the purposes of conservation marine flora, fauna, habitats, habitat types or features of geological or geomorphological interest.

The Habitats Regulations require that SACs are managed in a way that corresponds with the ecological requirements of the habitats and species for which the sites have been designated. The manner in which these sites should be managed and protected is set out in the Habitats Regulations. In summary, the designation of these sites requires the implementation of conservation measures.

The Scottish Government has been working to develop measures for the management of MPAs since they were designated, in addition to a review and development of management measures for marine SACs[24]. The inclusion of SACs stemmed from a re-evaluation of the implementation of the Habitats Directive[25].

2.3 Development of offshore fisheries management measures

Prior to the UK leaving the EU, the management of offshore MPAs was administered via the EU Common Fisheries Policy (CFP)[26]. According to Article 11 of the CFP, EU Member States are empowered to adopt conservation measures that are necessary to comply with their obligations under Article 6 of the Habitats Directive and Article 13(4) of the Marine Strategy Framework Directive (MSFD)[27].

Where measures are required outwith waters where the Member State has exclusive competence, the European Commission (EC) is empowered to adopt such measures by means of delegated acts. As was required, the UK was in the process of developing Joint Recommendations for submission to the EC, Advisory Councils and stakeholders in respect of the MPAs and SACs in the Scottish offshore region.

Scotland was required to follow this process in order to implement fisheries management measures for conservation purposes in the Scottish offshore region. This process, however, was not completed prior to the UK exiting the EU and, therefore, Scotland is now progressing offshore fisheries management using domestic processes and powers.

Scottish Government, following advice from JNCC, has identified MPAs and SACs in Scottish offshore waters that are considered to require fisheries management measures to ensure that they achieve their site conservation objectives. In total, 10 SACs and 10 NCMPAs, have been identified as requiring fisheries management measures. The location of the offshore MPAs that fisheries management measures are proposed for is shown in Figure 1.

The protected features and fisheries management measures that are proposed at these sites are set out in Table 1.

The development of the proposed management measures has been informed by advice from JNCC on the sensitivity of the protected features at each site as well as on possible management options and associated risks. Several sites have options for zonal measures, whereby only certain areas are subject to the proposed management measures and not the entirety of the site. Maps showing the zonal measures are included in Appendix B of the SEA Environmental Report7 and Appendix C of the SEIA8.

Details on the principles and process that have been followed to develop these measures is provided as part of the suite of documents on and implementation of fisheries management measures that has been published for public consultation.

The Marine and Coastal Access Act 2009 has been amended by the Fisheries Act 2020 to allow Scottish Ministers to make orders for the purpose of conserving marine flora, fauna or habitats, or features of geological or geomorphological interest. The Marine and Coastal Access Act 2009 and Sea Fish (Conservation) Act 1967 will be the legislative mechanisms used to implement the required fisheries management within the offshore MPAs and it is expected that the finalised measures will come into force in 2025.

The remaining MPAs that are not included in this round of management proposals are as follows:

  • Three SPAs for marine birds which are partially in the offshore region and are being taken forward as part of the fisheries management measures that are being developed for inshore MPAs;
  • Hatton Bank SAC which is managed by North-east Atlantic Fisheries Commission (NEAFC) and is already considered to be well managed;
  • Hatton Rockall Basin MPA which is located in NEAFC waters and falls outside the existing bottom fishing area footprint;
  • North-west Orkney MPA which is designated for sandeel and does not require fisheries management measures because the seabed in this area prevents sandeel fishing from taking place; and
  • Turbot Bank MPA is also designated for Sandeel, however proposed measures were initially developed for the site which would prohibit targeted Sandeel fishing across the full area. However, in 2023, the Scottish Government consulted on a closure to all fishing for Sandeel in all Scottish waters. As a result of this consultation The Sandeel (Prohibition Of Fishing) (Scotland) Order 2024 came into force on 26 March 2024 ahead of the 2024 fishery season and applies to all vessels (UK and EU) fishing within Scottish waters. Therefore no site specific management measures are proposed for this site.

Turbot Bank MPA will still feature within this assessment and the wider package of consultation documents which were prepared before the sandeel fisheries closure. Removing the site from the documents is not considered practical at this stage. This is because in addition to site specific assessments, overall assessments have been undertaken for the impacts of implementing measures as a full package.

Table 1 Offshore MPAs for which two management measures options are proposed

Site name

Protected feature

Option 1

Option 2

Northern North Sea (NNS)

Central Fladen MPA

Burrowed Mud

Zonal exclusion of demersal mobile gears.

Demersal mobile gears prohibited throughout the site.

East of Gannet and Montrose Field MPA

Offshore deep-sea muds

Mechanised dredge and beam trawling prohibited throughout site.

Zonal exclusion of demersal trawls.

Full site exclusion of mechanised dredge, beam trawls and demersal trawls.

Ocean quahog aggregations (including sands and gravels as their supporting habitat)

Faroe-Shetland Sponge Belt MPA

Deep-sea sponge aggregations

Zonal exclusion of demersal mobile and demersal static gears.

Demersal mobile and demersal static gears prohibited throughout site.

Offshore subtidal sands and gravels

Ocean quahog aggregations

Firth of Forth Banks Complex MPA

Ocean quahog aggregations

Zonal exclusion of beam trawls, demersal trawls and mechanised dredges.

Full site exclusion of beam trawls, demersal trawls and mechanised dredges

Offshore subtidal sands and gravels

Northeast Faroe-Shetland Channel MPA

Deep-sea sponge aggregations

Zonal exclusion of demersal mobile and demersal static gears.

Demersal mobile and demersal static gears prohibited throughout site.

Offshore sands and gravel

Deep sea muds

Norwegian Boundary Sediment Plain MPA

Ocean quahog aggregations (including sands and gravels as their supporting habitat)

Mechanised dredges, beam trawls and demersal trawls (including pair trawls/seines) prohibited from the whole site.

Zonal exclusion of demersal seines.

Demersal mobile gears prohibited throughout site.

Pobie Bank Reef SAC

Bedrock and stony reef

Zonal exclusion of demersal mobile gears.

Demersal mobile gears prohibited throughout site.

Northwest Waters (NWW)

East Rockall Bank SAC

Stony, bedrock and biogenic reef

Demersal mobile gears prohibited from zone covering 94% of site.

Demersal static gears prohibited in areas of known/predicted biogenic reef.

Demersal mobile and demersal static gears prohibited throughout site.

Geikie Slide and Hebridean Slope MPA

Burrowed mud (sea pens and burrowing megafauna)

Zonal exclusion of demersal mobile gears.

Demersal mobile gears prohibited throughout site.

Offshore subtidal sands and gravels

Offshore deep-sea muds

Northwest Rockall Bank SAC

Stony and biogenic reef

Zonal exclusion of demersal mobile and demersal static gears across 98% of the site.

Demersal mobile and demersal static gears prohibited throughout site.

Solan Bank Reef SAC

Bedrock and stony reef

Mechanised dredges and beam trawls prohibited throughout site.

Demersal trawls and seines prohibited within the site, except September and October where demersal trawls and seines are permitted within designated zone.

Demersal mobile gears prohibited throughout site.

Stanton Banks SAC

Bedrock and stony reef

Zonal exclusion of demersal mobile gears.

Demersal mobile gears prohibited throughout site.

The Barra Fan and Hebrides Terrace Seamount MPA

Seamount communities

Demersal mobile gears prohibited throughout site.

Demersal static gear prohibited from seamount feature.

Demersal mobile gears and demersal static gears prohibited throughout site.

Offshore sands

Deep sea muds

West Shetland Shelf MPA

Offshore subtidal sands and gravels

Dredges and beam trawls prohibited throughout site.

Zonal exclusion of demersal trawls and seines.

Demersal mobile gears prohibited throughout site.

Wyville-Thomson Ridge SAC

Stony and bedrock reef

Dredges and beam trawls prohibited throughout site.

Zonal exclusion of demersal trawls and seines.

Demersal mobile gears prohibited throughout site.

Table 2 Offshore MPAs for which one management measure option is proposed

Site name

Protected feature

Proposed management

Anton Dohrn Seamount MPA

Stony, bedrock and biogenic reef

Demersal mobile gears and demersal static gears prohibited throughout site.

Braemar Pockmarks SAC

Submarine structures made by leaking gases

Demersal mobile and demersal static gears prohibited throughout site.

Darwin Mounds SAC

Stony, bedrock and biogenic reef

Demersal mobile and demersal static gears prohibited throughout site.

Scanner Pockmark SAC

Submarine structures made by leaking gases

Demersal mobile gears and demersal static gears prohibited throughout site.

Turbot Bank MPA

Sandeels

Targeted fishing for sandeel prohibited throughout site.

West of Scotland NCMPA

Burrowed mud

Demersal mobile and demersal static gears prohibited throughout site.

Deep-sea sponge aggregations

Coral gardens

Cold-water coral reefs

Offshore deep-sea muds

Offshore subtidal sands and gravels

Seamount communities

2.4 Policy context overview of proposals for offshore fisheries management measures

The 2004 Regulations require that Responsible Authorities define the plan’s broader policy context, particularly any relevant environmental protection objectives that will influence the plan’s development and implementation. This assessment has been conducted in line with that requirement.

The immediate policy context for the proposed management measures is described in Sections 2.1 to 2.4 and listed below. Appendix A of the SEA includes a detailed review of the broader policy context in which the proposed management measures sit, beginning with a summary of relevant marine policies and followed by an overview of policies relating to the SEA topics that have been scoped into the assessment: Biodiversity, Flora and Fauna; Soil (assessed under Biodiversity, Flora and Fauna); Water (assessed under Biodiversity, Flora and Fauna); and Climatic Factors (assessed under Biodiversity, Flora and Fauna) (Section 3.2).

The key legislative and policy context for implementing fisheries management measures in NCMPAs and SACs is:

  • Marine and Coastal Access Act 2009 (Offshore NCMPAs)
  • Sea Fish (Conservation) Act 1967 (Inshore NCMPAs)
  • Habitats Regulations 2017 (SACs)
  • UK Marine Strategy
  • National Marine Plan
  • OSPAR Convention.

Contact

Email: marine_biodiversity@gov.scot

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