Fisheries Management Measures within Scottish Inshore Marine Protected Areas (MPAs) and Proposed Priority Marine Feature (PMF) Management Areas - High level Site Summary Details and Potential Impacts of Proposed Fisheries Management Measures

Overview of site and area details and potential impacts of the proposed fisheries management measures within Scottish Inshore Marine Protected Areas (MPAs) and proposed Priority Marine Feature (PMF) management areas


12. Moray Firth Scottish Marine Region MPAs

Due to the complexity and large number of areas and sites, ecosystem services data has been produced at a regional level, allowing for a more consistent assessment across wider geographical scales while still capturing key variations in ecological, social, and economic value.

Table 27: Estimated Ecosystem Service Impacts of proposed fisheries management measures (over 20 years) for Moray Firth Region

Total value of changes in ecosystem services

Option 1 Min

Option 1 Max

Option 2 Min

Option 2 Max

Benefits

Moderate

Moderate

High

High

Costs

Minimal

Low

Very High

Potential to displace negative ES effects

Very High

Net Impacts

Low Benefit

Low Benefit

Moderate Cost

Moderate Cost

12.1. Site: Southern Trench NCMPA

Protected features:

  • Burrowed mud
  • Fronts
  • Minke whale
  • Quaternary of Scotland
  • Shelf deeps
  • Submarine Mass Movement

Fronts, shelf deeps, Quaternary of Scotland and submarine mass movement are not discussed further as they are not a protected feature for which fisheries management measures are required.

Feature conditions:

  • Burrowed mud - Favourable
  • Minke whale - Favourable

Conservation objectives:

  • Burrowed mud - Conserve
  • Minke whale - Conserve

The proposed management measures for Southern Trench NCMPA are as follows:

Option 1:

  • Demersal trawls, demersal seine nets, beam trawls and mechanical dredge prohibited by vessels with engine power greater than 500kw in burrowed mud part of the site
  • Set nets prohibited from June till end of October (not including fyke nets) in part of the site that doesn’t overlap with any other site
  • Set nets (including fyke nets) prohibited in overlapping portion with the Moray Firth SPA that’s shallower than 64.5m
  • Demersal set nets (including fyke nets) prohibited from June till end of October and pelagic set nets prohibited in part of the site that overlaps with the Moray Firth SPA that’s deeper than 64.5m
  • Longlines (until technical measures come into force) and set nets (including fyke nets) from February till end of October prohibited in part of the site that overlaps with the Troup, Pennan and Lion’s Heads SPA
  • Full site closure to hydraulic dredge

Figure 54. Map of measures proposed under option 1:

Option 1 map shows the Southern Trench Nature Conservation Marine Protected Area (NCMPA) covering an area off the coast between Buckie and Peterhead extending 30km outwards to a depth below 80m in most parts. A large band of burrowed mud runs through the north of the site. Hydraulic dredges are prohibited throughout the site. This site has further zoned measures, divided into 5 zones. The burrowed mud band is covered wholly by a zone prohibiting use of demersal mobile gear (excluding hydraulic dredges which are fully prohibited) by vessels with engine power greater than 500kw, with set nets (not including fyke nets) prohibited from June to the end of October. A small area south of the burrowed mud north of Buckie prohibits demersal set nets (including fyke nets) from June to the end of October and pelagic set nets year round. The westernmost area of the NCMPA shallower than 80m as far east as Portsoy prohibits set nets (including fyke nets) year round. A small area around Troup head and stretching a small way past Pennan prohibits longlines (until technical measures come into force), with set nets (including fyke nets) prohibited June to the end of October. The remainder of the site prohibits set nets (not including fyke nets) June to the end of October.

Option 2*

  • Full site closure to demersal mobile gears (demersal trawls, demersal seine nets, beam trawls, mechanical dredge and hydraulic dredge) and set nets (not including fyke nets)

Figure 55. Map of measures proposed under option 2:

Option 2 map shows the Southern Trench Nature Conservation Marine Protected Area (NCMPA) covering an area off the coast between Buckie and Peterhead extending 30km outwards to a depth below 80m in most parts. A large band of burrowed mud runs through the north of the site. A full site prohibition applies to all demersal mobile gear and set nets (not including fyke nets).

*The measures for Option 2 proposals only come from gear types prohibited in non-overlapping areas. Overlapping restrictions may still apply from overlapping sites or areas dependent on the decisions taken for that site or area.

Overlapping sites included in this consultation

This NCMPA overlaps with the Moray Firth SPA and Troup, Pennan and Lion’s Head SPA.

Table 28: Estimated Socio-economic impacts of proposed measures for Southern Trench NCMPA

Socio-Economic Impact

Option 1

Option 2

Average annual loss in value of landings (£000s, 2022 prices)

2.1 - 150.6

5,433.8 - 5,433.8

Direct + indirect reduction in GVA (PV) impact (£000s) 20 years

1.9 - 1,052.9

38,479.7 - 38,479.7

Average (mean) number of direct + indirect jobs (year on year, over 20 years), Full Time Equivalents

0 - 1.7

61.6 - 61.6

Table 29: Estimated Environmental impacts of proposed fisheries management measures for Southern Trench NCMPA

Environmental Impact

Option 1

Option 2

Benefits within the sites/areas

Major beneficial

Major beneficial

Spill over benefits

Negligible beneficial

Moderate beneficial

Displacement effects

Negligible adverse

Moderate adverse

Effects from other gear types

Negligible adverse

Minor adverse

Estimated overall environmental impact

Benefit

Benefit

12.2. Site: East Caithness Cliffs NCMPA and East Caithness Cliffs SPA

Protected features:

NCMPA:

  • Black guillemot - breeding and non-breeding.

SPA:

  • Cormorant - breeding
  • Fulmar - breeding
  • Great black-backed gull - breeding
  • Guillemot - breeding
  • Herring gull - breeding
  • Kittiwake - breeding
  • Peregrine - breeding
  • Razorbill - breeding
  • Shag – breeding

Peregrine are not discussed further as they are not a protected feature for which fisheries management measures are required.

Feature conditions:

NCMPA:

  • Black guillemot – Unfavourable

SPA:

  • Cormorant - Unfavourable
  • Fulmar - Favourable
  • Great black-backed gull - Unfavourable
  • Guillemot - Favourable
  • Herring gull - Unfavourable
  • Kittiwake - Favourable
  • Razorbill - Favourable
  • Shag - Unfavourable

Conservation objectives:

NCMPA:

  • Black guillemot – Recover

SPA:

  • Cormorant - Restore
  • Fulmar - Maintain
  • Great black-backed gull - Restore
  • Guillemot - Maintain
  • Herring gull - Restore
  • Kittiwake - Maintain
  • Razorbill - Maintain
  • Shag - Restore

The proposed management measure for East Caithness Cliffs NCMPA and SPA is as follows:

Single Proposed Management Option:

  • Full site closure to longlines (until technical measures come into force), set nets (including fyke nets) and hydraulic dredge.

Figure 56. Map of measures proposed:

Single proposed option map shows East Caithness Cliffs SPA and NCMPA, a strip of water hugging the cliffs between Helmsdale and Wick. Longlines (until technical measures come into force), set nets (including fyke nets), and hydraulic dredges are prohibited throughout.

A full site level of protection from the specified gear has been identified as the only suitable option in enabling the achievement of the desired level of protection for the feature in question.

Overlapping sites included in this consultation

This NCMPA and SPA overlaps with the Moray Firth SPA

Estimated Socio-economic impacts of proposed measures for East Caithness Cliffs NCMPA and East Caithness Cliffs SPA

No socio-economic impacts are anticipated for this site, based on available data in relation to:

  • Average annual loss in value of landings (£000s, 2022 prices)
  • Direct + indirect reduction in GVA (PV) impact (£000s) 20 years
  • Average (mean) number of direct + indirect jobs (year on year, over 20 years), Full Time Equivalents
Table 30: Estimated Environmental impacts of proposed fisheries management measures for East Caithness Cliffs NCMPA and East Caithness Cliffs SPA

Environmental Impact

Single Proposed Management Option

Benefits within the sites/areas

Moderate beneficial

Spill over benefits

None

Displacement effects

None

Effects from other gear types

None

Estimated overall environmental impact

Benefit

12.3. Site: Dornoch Firth and Morrich More SAC and Moray Firth SAC

Protected features:

Dornoch Firth and Morrich More SAC:

  • Estuaries
  • Harbour Seal
  • Intertidal mudflats and Sandflats
  • Reefs
  • Otter
  • Subtidal sandbanks

Moray Firth SAC:

  • Bottlenose dolphin
  • Subtidal sandbanks

Otter is not discussed further as they are not a protected feature for which fisheries management measures are required.

Feature conditions:

Dornoch Firth and Morrich More SAC:

  • Estuaries - Not Assessed
  • Harbour Seal - Unfavourable
  • Intertidal mudflats and Sandflats - Favourable
  • Reefs - Unfavourable
  • Subtidal sandbanks – Favourable

Moray Firth SAC:

  • Bottlenose dolphin - Favourable
  • Subtidal sandbanks - Favourable

Conservation objectives:

Dornoch Firth and Morrich More SAC:

  • Estuaries - Maintain
  • Harbour Seal - Restore
  • Intertidal mudflats and Sandflats - Maintain
  • Reefs - Restore
  • Subtidal sandbanks – Maintain

Moray Firth SAC:

  • Bottlenose dolphin - Maintain
  • Subtidal sandbanks - Maintain
  • Demersal trawl, demersal seine net, beam trawl, mechanical dredge, hydraulic dredge, pelagic seine (including ring-nets) and set nets (including fyke nets) prohibited (Hatching 5)

The proposed management measures for Dornoch Firth and Morrich More and Moray Firth SAC are as follows:

Option 1:

  • Beam trawl, set nets (including fyke nets) and hydraulic dredge prohibited (Hatching 1)
  • Beam trawl, set nets (including fyke nets), mechanical dredges and hydraulic dredge prohibited (Hatching 2)
  • Beam trawl, set nets (not including fyke nets) and hydraulic dredge prohibited (Hatching 3)
  • Demersal trawl, demersal seine net, beam trawl, mechanical dredge, hydraulic dredge, set nets (including fyke nets) and pelagic seine (including ring-nets) prohibited (Tain Mussel Fishery exempt) (Hatching 4)
  • Demersal trawl, demersal seine net, beam trawl, set nets (including fyke nets), mechanical dredges and hydraulic dredge prohibited (Hatching 6)

Figure 57. Map of measures proposed under option 1:

Option 1 map of Dornoch Firth and Morrich More and Moray Firth Special Areas of Conservation (SACs). The area contains estuaries around Tain in the Dornich Firth, with intertidal mudflats and sandflats along the edges of this firth, with reefs in the centre of the firth. subtidal sandbanks cover most of the remaining coastal areas, particularly in the Moray Firth itself.. The area is zoned into 6 areas with differing measures, these measures are not defined on the map.

Option 2*

  • Full site closure for both SACs to hydraulic dredge, demersal trawls and seine, beam trawl and mechanical dredge. (Tain mussel fishery exempt)
  • Full site closure to set nets (including fyke nets) and pelagic seine (including ring-nets) for Dornoch Firth and Morrich More SAC
  • Full site closure to set nets (not including fyke nets) for Moray Firth SAC

Figure 58. Map of measures proposed under option 2:

Option 2 map of Dornoch Firth and Morrich More and Moray Firth Special Areas of Conservation (SACs) The area contains estuaries around Tain in the Dornoch Firth, with intertidal mudflats and sandflats along the edges of this firth, with reef in the centre of the firth. Subtidal sandbanks cover most of the remaining coastal areas, particularly in the Moray Firth itself. The remainder of the Dornich Firth and Morrick More SAC (which ends where the firth opens) prohibits all demersal mobile gear, set nets (including fyke nets) and pelagic seine (including ring nets). The Tain Mussel Fishery (covering most of the open area of the Dornoch Firth near Tain is exempt). Throughout the rest of the area, covering the Moray Firth SAC, all demersal mobile gear, and set nets (not including fyke nets) are prohibited.

*The measures for Option 2 proposals only come from gear types prohibited in non-overlapping areas. Overlapping restrictions may still apply from overlapping sites or areas dependent on the decisions taken for that site or area.

Overlapping sites included in this consultation

These SACs overlap with the Moray Firth SPA.

Table 31: Estimated Socio-economic impacts of proposed measures for Dornoch Firth and Morrich More SAC and Moray Firth SAC

Socio-Economic Impact

Option 1

Option 2

Average annual loss in value of landings (£000s, 2022 prices)

0.8 - 33.4

1,974.2 - 1,974.2

Direct + indirect reduction in GVA (PV) impact (£000s) 20 years

6.3 - 247.1

14,513.9 - 14,514.2

Average (mean) number of direct + indirect jobs (year on year, over 20 years), Full Time Equivalents

0 - 0.4

22.4 - 22.4

Table 32: Estimated Environmental impacts of proposed fisheries management measures for Dornoch Firth and Morrich More SAC and Moray Firth SAC

Environmental Impact

Option 1

Option 2

Benefits within the sites/areas

Moderate beneficial

Major beneficial

Spill over benefits

Negligible beneficial

Minor beneficial

Displacement effects

Negligible adverse

Minor adverse

Effects from other gear types

Negligible adverse

Minor adverse

Estimated overall environmental impact

Benefit

Benefit

12.4. Site: Moray Firth SPA

Protected features:

  • Common scoter - non-breeding
  • Eider - non-breeding
  • Goldeneye - non-breeding
  • Great northern diver - non-breeding
  • Long-tailed duck - non-breeding
  • Red-breasted merganser - non-breeding
  • Red-throated diver - non-breeding
  • Scaup - non-breeding
  • Shag – breeding and non-breeding
  • Slavonian grebe - non-breeding
  • Velvet scoter - non-breeding

Feature conditions:

  • Common scoter - Favourable
  • Eider - Favourable
  • Goldeneye - Favourable
  • Great northern diver - Favourable
  • Long-tailed duck - Favourable
  • Red-breasted merganser - Favourable
  • Red-throated diver - Favourable
  • Scaup - Favourable
  • Shag – unfavourable at breeding colony SPA, Favourable in non-breeding season
  • Slavonian grebe - Favourable
  • Velvet scoter - Favourable

Conservation objectives:

  • Common scoter - Maintain
  • Eider - Maintain
  • Goldeneye - Maintain
  • Great northern diver - Maintain
  • Long-tailed duck - Maintain
  • Red-breasted merganser - Maintain
  • Red-throated diver - Maintain
  • Scaup - Maintain
  • Shag - Restore
  • Slavonian grebe - Maintain
  • Velvet scoter - Maintain

The proposed management measures for Moray Firth SPA are as follows:

Option 1:*

  • Set nets (including fyke nets) prohibited in areas down to 64.5m and pelagic set nets prohibited in areas deeper than 64.5m based on presence and maximum dive depth of shag
  • Longlines (until technical measures come into force) prohibited in part of the site that overlaps with the East Caithness Cliffs SPA
  • Pelagic seine (including ring-nets) prohibited in part of the site that overlaps with the Dornoch Firth and Morrich More SAC
  • Demersal set nets (not including fyke nets) prohibited from June till end of October and pelagic set nets prohibited in overlapping area with Southern Trench NCMPA deeper than 64.5m based on presence and maximum dive depth of shag and static net seasonal measures for minke whale from the NCMPA
  • Full site closure to hydraulic dredge

Figure 59. Map of measures proposed under option 1:

Map shows Moray Firth SPA, a site extending seaward from the Helmsdale coast in the north to Portsoy in the east. It includes the outer Dornoch and Cromarty Firths, Beauly and Inverness Firths, as well as part of the wider Moray Firth. Almost all of the site is shallower than 64.5m, with only small areas in the southeast (north of Elgin and Buckie) being deeper. In the shallower majority of the site set nets (including fyke nets) are prohibited. In the deeper areas pelagic set nets are prohibited year-round. Pelagic seine (including ring-nets) prohibited in the part of the site that overlaps with the Dornoch Firth and Morrich More SAC. Demersal set nets (not including fyke nets) from June till end of October and pelagic set nets are prohibited in the area overlapping Southern Trench NCMPA deeper than 64.5m. Throughout the site hydraulic dredges are prohibited.

*This site will have other demersal mobile measures that may apply from the overlapping portions with the Dornoch Firth and Morrich More and Moray Firth SACs that aren’t shown on the map for this option.

  • Dornoch Firth and Morrich More SAC would prohibit demersal trawls and seines, beam trawls and mechanical dredge in the overlapping areas. Mechanical dredge exempt in Tain Mussel Fishery.
  • Moray Firth SAC has zoned areas so demersal trawls and seines, beam trawls and mechanical dredge could be prohibited in overlapping areas.

Please check the Option 1 overlapping site map to see proposed demersal mobile measures under Option 1.

Option 2:*

  • Full site closure to set nets (including fyke nets) and hydraulic dredge.

Figure 60. Map of measures proposed under option 2:

Map shows Moray Firth SPA, a site extending seaward from the Helmsdale coast in the north to Portsoy in the east. It includes the outer Dornoch and Cromarty Firths, Beauly and Inverness Firths, as well as part of the wider Moray Firth. Throughout the site set nets (including fyke nets) and hydraulic dredges are prohibited.

*The measures for Option 2 proposals only come from gear types prohibited in non-overlapping areas. Overlapping restrictions may still apply from overlapping sites or areas dependent on the decisions taken for that site or area.

Overlapping sites included in this consultation

This SPA overlaps with the East Caithness Cliffs and Southern Trench NCMPAs Dornoch Firth and Morrich More and Moray Firth SACs and East Caithness Cliffs SPA.

Estimated Socio-economic impacts of proposed measures for Moray Firth SPA

No socio-economic impacts are anticipated for this site, based on available data in relation to:

  • Average annual loss in value of landings (£000s, 2022 prices)
  • Direct + indirect reduction in GVA (PV) impact (£000s) 20 years
  • Average (mean) number of direct + indirect jobs (year on year, over 20 years), Full Time Equivalents
Table 33: Estimated Environmental impacts of proposed fisheries management measures for Moray Firth SPA

Environmental Impact

Option 1

Option 2

Benefits within the sites/areas

Major beneficial

Major beneficial

Spill over benefits

None

None

Displacement effects

None

None

Effects from other gear types

None

None

Estimated overall environmental impact

Major benefit

Major benefit

12.5. Site: Troup, Pennan and Lion`s Heads SPA

Protected features:

  • Fulmar - breeding
  • Guillemot - breeding
  • Herring gull - breeding
  • Kittiwake - breeding
  • Razorbill - breeding

Feature conditions:

  • Fulmar - Unfavourable
  • Guillemot - Unfavourable
  • Herring gull - Unfavourable
  • Kittiwake - Unfavourable
  • Razorbill - Favourable

Conservation objectives:

  • Fulmar - Restore
  • Guillemot - Restore
  • Herring gull - Restore
  • Kittiwake - Restore
  • Razorbill - Maintain

The proposed management measures for Troup, Pennan and Lion’s Head SPA are as follows:

Option 1:

  • Set nets (including fyke nets) prohibited February till end of August in areas down to 177m based on presence and maximum dive depth for guillemot
  • Set nets (including fyke nets) prohibited February till end of October in areas overlapping the Southern Trench NCMPA
  • Full site closure to longlines (until technical measures come into force) and hydraulic dredge.

Figure 61. Map of measures proposed under option 1:

Map shows Troup, Pennan and Lion's Heads SPA- which covers an area of coast running from the peninsula southwest of Rosehearty to the peninsula west of Gardenstown. The entire site is shallower than 177m. Across the site set nets are prohibited February to end of August, this prohibition extends to the end of October in areas overlapping the Southern Trench NCMPA (which account for the majority of the site- covering all but the areas immediately adjacent to the coast). Throughout the year hydraulic dredges and longlines (until technical measures come into force) are prohibited across the whole site.

Option 2:

  • Full site closure to longlines (until technical measures come into force), set nets (including fyke nets) and hydraulic dredge.

Figure 62. Map of measures proposed under option 2:

Map shows Troup, Pennan and Lion's Heads SPA- which covers an area of coast running from the peninsula southwest of Rosehearty to the peninsula west of Gardenstown. Set nets (including fyke nets), longlines (until technical measures come into force) and hydraulic dredges are prohibited throughout the site.

Overlapping sites included in this consultation

This SPA overlaps with the Southern Trench NCMPA.

Estimated Socio-economic impacts of proposed measures for Troup, Pennan and Lion`s Heads SPA

No socio-economic impacts are anticipated for this site, based on available data in relation to:

  • Average annual loss in value of landings (£000s, 2022 prices)
  • Direct + indirect reduction in GVA (PV) impact (£000s) 20 years
  • Average (mean) number of direct + indirect jobs (year on year, over 20 years), Full Time Equivalents
Table 34: Estimated Environmental impacts of proposed fisheries management measures for Troup, Pennan and Lion`s Heads SPA

Environmental Impact

Option 1

Option 2

Benefits within the sites/areas

Moderate beneficial

Moderate beneficial

Spill over benefits

None

None

Displacement effects

None

None

Effects from other gear types

None

None

Estimated overall environmental impact

Benefit

Benefit

Contact

Email: marine_biodiversity@gov.scot

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