Draft Fisheries Assessment – West of Scotland NCMPA: Fisheries management measures within Scottish Offshore Marine Protected Areas (MPAs)
These assessments look at the fishing activity occurring within each offshore MPA and SAC and assess the potential impacts of this activity on the protected features within each site. This assessment is for West of Scotland NCMPA.
2. Part A assessment – fisheries screening
2.1 Fisheries screening overview
Part A of this assessment considers whether the fishing activity would be capable of affecting the protected features of an NCMPA or any ecological or geomorphological process on which the conservation of any protected feature is dependent. This section looks at the pressures exerted by the fishing activity occurring in the site (within the assessment period) in relation to the sensitivities of the protected features. Activities potentially capable of affecting the protected feature were identified where there was both a medium-high risk of a pressure arising from the fishing activity and if any of the features were considered sensitive to that pressure. These pressure-features interactions were then taken forward to the fisheries assessment stage (Part B) to determine whether the fishing activity in question would or might hinder the achievement of the conservation objectives.
For each activity assessed in Part A, there were two possible outcomes for each identified pressure-feature interaction:
- The pressure-feature interactions were not included for Part B:
- If the feature is not exposed to the pressure, and is not likely to be in the future; or
- If the effect/impact of the pressure is non-existent or insignificant.
- The pressure-feature interactions were included for assessment in Part B:
- If the feature is exposed to the pressure, or is it likely to be in the future; and
- If the pressure is capable of affecting the feature; or
- If it is not possible to determine whether the pressure is capable of affecting the feature.
Part B of the assessment considers the potential for activities to affect the feature by assessing the impact of fishing gears identified in Part A. This involves determining the potential level of interaction between the feature and the fishing activity, assessing the potential impact on the feature, and subsequently if fishing activities would or might hinder the achievement of the conservation objectives for the site.
Consideration of exposure to and the effect of a pressure on a protected feature of the NCMPA includes the consideration of exposure to and the effect of that pressure on any ecological or geomorphological process on which the conservation of the protected feature is wholly or in part dependant.
The JNCC West of Scotland NCMPA Conservation Objectives and Management Advice document and the West of Scotland NCMPA Fisheries Management Options paper have been used to inform this assessment. This is the most recent information and options paper available.
Where appropriate, this advice has been supplemented by information on pressures associated with fishing activity from the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022 and the Feature Activity Sensitivity Tool (FeAST).
2.2 Activities taking place within West of Scotland NCMPA
To screen out fishing activities that were not taking place within the site or likely to take part in the future, Vessel Monitoring System (VMS) data within West of Scotland NCMPA from 2015 – 2019 were analysed to identify the gear types being used in the site and the aggregated gear method (Table 1). The fishing gears screened out at this stage were not taken forward to Part B of the assessment.
On reviewing the ICES gridded data, which includes EU and Norwegian vessels, demersal seine activity was also found to occur within the site.
Gear type | Specific Gear Type | Gear code | Aggregated gear method |
---|---|---|---|
Towed | Bottom otter trawl | OTB | Demersal trawls |
Multi-rig trawls | OTT | ||
Bottom trawls (not specified) | TB | ||
Towed (pelagic) | Mid-water trawl (single) | OTM | Pelagic fishing |
Static- fixed nets | Set gillnets | GNS | Anchored nets/lines |
Lines | Set longlines | LLS |
2.3 Potential pressures exerted by site fishing activity
According to the JNCC West of Scotland NCMPA Management Options Paper (2023) the existing fishing activity believed to take place within or close to West of Scotland NCMPA considered capable of affecting the protected features are demersal trawls; demersal seines; purse seines; pelagic trawls; unknown trawls; gillnets; hooks and lines and pots and traps.
The potential pressures that could be exerted by fishing activities (demersal trawls, pelagic fishing, anchored nets/lines and demersal seines) considered capable of affecting protected features were determined using information on activity-pressure relationships in the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022. The potential pressures that could be exerted by demersal trawls, pelagic fishing, anchored nets/lines and demersal seines are summarised in Table 2.
The aggregated gear type of ‘anchored nets/lines’ spans two categories in the PAD: set (fixed) net fishing and line fishing. Subsequently, potential pressures for this aggregated gear type were listed under the two PAD categories (Table 2). The risk profiling of pressures was the same for set (fixed) net fishing and line fishing within PAD, confirming that these categories could be considered together under the aggregated gear type of ‘anchored nets/lines’ in later sections of the assessment.
Within the PAD, the above water noise and collision above water pressures both had low risk profiles for all fishing activity types, however these were not considered capable of affecting the protected features and were excluded.
PAD Pressure | Demersal trawls | Demersal seines | Pelagic fishing | Anchored nets/lines |
---|---|---|---|---|
Transition elements and organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC | Low | Low | Low | Low |
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Low | Low | Low | Low |
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Low | Low | Low | Low |
Deoxygenation | Low | Low | Low | Low |
Nutrient enrichment | Low | Low | Not relevant | Not relevant |
Organic enrichment | Low | Low | Low | Low |
Physical change (to another seabed type) | Low | Low | Not relevant | Not relevant |
Physical change (to another sediment type) | Low | Low | Not relevant | Not relevant |
Abrasion/disturbance of the substrate on the surface of the seabed | Medium-high | Medium-high | Not relevant | Medium-high |
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion | Medium-high | Medium-high | Not relevant | Low |
Changes in suspended solids (water clarity) | Medium-high | Medium-high | Not relevant | Not relevant |
Smothering and siltation rate changes (Light) | Medium-high | Medium-high | Not relevant | Not relevant |
Litter | Low | Low | Low | Low |
Underwater noise changes | Low | Low | Low | Low |
Introduction of light | Low | Low | Low | Low |
Barrier to species movement | Not relevant | Not relevant | Low | Low |
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g. boats, machinery and structures) | Low | Low | Low | Low |
Visual disturbance | Low | Low | Low | Low |
Introduction or spread of invasive non-indigenous species (INIS) | Low | Low | Low | Low |
Removal of target species | Medium-high | Medium-high | Medium-high | Medium-high |
Removal of non-target species | Medium-high | Medium-high | Medium-high | Medium-high |
2.4 Significance of effects/impacts to protected features
In the absence of a JNCC Advice on Operations advice package for this site, the Feature Activity Sensitivity Tool (FeAST) and JNCC Marine Pressures-Activities Database (PAD) v1.5 2022 were used to determine the potential sensitivity of the protected features (Table 3) to the pressures exerted by the relevant fishing activities (Table 2).
Table 3 identifies the pressures from particular gears that could be capable of affecting each feature. Where a pressure from a particular gear is identified as being capable of affecting a feature, justification is provided. To ensure the effects of fishing activities in-combination with other activities (including other fishing activities) are fully assessed, the pressures from fishing activities which were not identified being capable of affecting a feature but which do interact with the feature are considered in the in-combination aspect of the assessment (Part C).
Potential pressures | Burrowed mud (including sea-pens) | Coral gardens | Cold-water coral reefs (including Lophelia pertusa reefs) | Deep-sea sponge aggregations | Offshore deep-sea muds | Offshore sands and gravels | Seamount communities |
---|---|---|---|---|---|---|---|
Abrasion/disturbance of the substrate on the surface of the seabed | Medium Sensitivity | High sensitivity | Not assessed | High sensitivity | High sensitivity* | High sensitivity | High sensitivity |
Changes in suspended solids (water clarity) | Low | Sensitive | Not assessed | Sensitive | Not Exposed | Not Exposed | Sensitive |
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g., boats, machinery, and structures) | No Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Deoxygenation | Low | Not Exposed | Not Assessed | Not Exposed | Not Exposed | Not Exposed | Not Exposed |
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not Assessed | Sensitive | Sensitive | Sensitive | Sensitive |
Introduction of light | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Introduction or spread of invasive non-indigenous species (INIS) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Sensitive | Not Assessed |
Litter | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Nutrient enrichment | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Sensitive | Not Sensitive | Not Assessed |
Organic enrichment | Medium Sensitivity | High Sensitivity | Not assessed | High Sensitivity | High Sensitivity | High Sensitivity | Not Assessed |
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion | Medium Sensitivity | High Sensitivity | Not Assessed | High Sensitivity | High Sensitivity | High Sensitivity | High Sensitivity |
Physical change (to another seabed type) | High Sensitivity | High Sensitivity | Not Assessed | High Sensitivity | High Sensitivity | High Sensitivity | High Sensitivity |
Physical change (to another sediment type) | High Sensitivity | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not assessed |
Removal of non-target species | Medium Sensitivity* | High Sensitivity | Not Assessed | High Sensitivity | High Sensitivity | High Sensitivity | High Sensitivity |
Removal of target species | Medium Sensitivity | Not Exposed | Not Assessed | Not Exposed | Not Exposed | Not Exposed | Not Exposed |
Smothering and siltation rate changes (Light) | Low | High Sensitivity | Not Assessed | High Sensitivity | High Sensitivity | High Sensitivity* | High Sensitivity |
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not Assessed | Sensitive | Sensitive | Sensitive | Sensitive |
Transition elements & organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not assessed | Sensitive | Sensitive | Sensitive | Sensitive |
Underwater noise changes | Not Sensitive | Sensitive | Not assessed | Sensitive | Not sensitive | Not sensitive | Sensitive |
Visual disturbance | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Potential pressures | Orange roughy | Blue ling | Round-nose grenadier | Leafscale gulper shark/Gulper shark | Portuguese dogfish |
---|---|---|---|---|---|
Abrasion/disturbance of the substrate on the surface of the seabed | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Barrier to species movement | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Changes in suspended solids (water clarity) | Not Sensitive | Not Sensitive | Not Assessed | Not Assessed | Not Assessed |
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g., boats, machinery, and structures) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Deoxygenation | Not Exposed | Not Exposed | Not Assessed | Not Assessed | Not Assessed |
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not Assessed | Not Assessed | Not Assessed |
Introduction of light | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Introduction or spread of invasive non-indigenous species (INIS) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Litter | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Nutrient enrichment | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Organic enrichment | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Physical change (to another seabed type) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Physical change (to another sediment type) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Removal of non-target species | Low Sensitivity | Medium Sensitivity | Not Assessed | Not Assessed | Not Assessed |
Removal of target species | High Sensitivity | High Sensitivity | Not Assessed | Not Assessed | Not Assessed |
Smothering and siltation rate changes (Light) | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not Assessed | Not Assessed | Not Assessed |
Transition elements & organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | Sensitive | Sensitive | Not Assessed | Not Assessed | Not Assessed |
Underwater noise changes | Not Sensitive | Not Sensitive | Not Assessed | Not Assessed | Not Assessed |
Visual disturbance | Not Assessed | Not Assessed | Not Assessed | Not Assessed | Not Assessed |
Considering both the information on the pressure activity association (Table 2) and the sensitivity of protected habitats features (Table 3) and protected mobile species features (Table 4) pressures that have the potential to affect the feature are summarised in Table 5. Table 3 and 4 list the sensitivity of the protected features to the pressures caused by each type of fishing gear occurring within West of Scotland NCMPA.
Table 5 identifies the pressures from particular gears that are capable of affecting each protected feature. Where a pressure from a particular gear is identified as not being capable of affecting the feature, justification is provided. Pressures with a medium-high risk profile in PAD and to which FeAST assessed the feature as being Sensitive, Medium Sensitivity or High Sensitivity have the potential to affect the feature.
Pressures that are not relevant to demersal trawls, demersal seines, pelagic fishing, and anchored nets/lines (pressures that are not exerted by that fishing activity: ‘not relevant to the activity’ in Table 4) do not need to be considered further in the assessment. According to the PAD methods document (Robson et al., 2018), pressures with low risk profiles (i.e. ‘low’ risk profile for the activity: Tables 2 & 4) generally do not occur at a level of concern and should not require consideration as part of an assessment, unless there are evidence-based cases or site-specific factors that increase the risk, or there is uncertainty on the level of pressure on a receptor. Pressures with ‘medium-high’ risk profiles are commonly induced by the activity at a level that needs to be considered further as part of an assessment.
Of all the pressures considered, six have medium-high risk profiles (PAD) for either all, or some of the fishing activities that occur within the site, and the protected features have are sensitive to either all, or some, of these pressures (FeAST). The six pressures are abrasion/disturbance of the substrate on the surface of the seabed; penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion; smothering and siltation rate changes (light); changes in suspended solids (water clarity); removal of target species and removal of non-target species (Table 5). These six pressures are subsequently considered to have the potential to affect a combination of the protected habitat and mobile species features. All six of these pressures are exerted by either all, or some of the fishing activities that occur within the site (demersal trawls, demersal seines, pelagic fishing and anchored nets/lines).
To ensure the effects of fishing activities in-combination with other activities (including other fishing activities) are fully assessed, the pressures from fishing activities which were not considered capable of affecting but which do interact with the features are considered in the in-combination aspect of the assessment (Part C).
Potential pressure | Demersal trawls | Demersal seines | Pelagic fishing | Anchored nets/lines |
---|---|---|---|---|
Transition elements and organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC | No – although some features may be sensitive, there is a low risk profile for the activities. | |||
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. | No - although some features may be sensitive, there is a low risk profile for the activities. | |||
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. | No - although some features may be sensitive, there is a low risk profile for the activities. | |||
Deoxygenation | No – the pressure has a low risk profile for the activities, and Burrowed mud has low sensitivity to this pressure (the other protected habitat and mobile species features are either not exposed or sensitivity is not assessed). | |||
Nutrient enrichment | No - low risk profile for demersal trawls and seines activities (and is not relevant for pelagic fishing or anchored nets/lines) and the protected habitat and mobile species features are either not assessed or not sensitive. | |||
Organic enrichment | No – although Coral gardens, Deep-sea sponge aggregations, Offshore deep-sea muds and Offshore sands and gravels have high sensitivity and Burrowed mud has medium sensitivity to this pressure, the pressure has a low risk profile for the activities (the mobile species features, and Seamount communities and Cold-water coral reefs are not assessed) | |||
Physical change (to another seabed type) | No – although the habitat features have high sensitivity to this pressure, the pressure has a low risk profile for demersal trawls and seines activities (and is not relevant for pelagic fishing or anchored nets/lines). Mobile species features and Cold-water coral reefs are not assessed. | |||
Physical change (to another sediment type) | No – although Burrowed mud has high sensitivity to this pressure, the pressure has a low risk profile for the demersal trawls and seines activities (and is not relevant for pelagic fishing or anchored nets/lines). Other protected habitat and mobile species features are not assessed. | |||
Abrasion/disturbance of the substrate on the surface of the seabed | Yes – the pressure has a Medium-high risk profile for demersal trawls, seines and anchored nets/lines (it is not relevant for pelagic fishing) AND the habitat features have either high sensitivity (Coral gardens, Deep-sea sponge aggregations, Offshore deep-sea muds, Offshore sands and gravels, and Seamount communities) of medium sensitivity (Burrowed mud) to this pressure (mobile species features and Cold-water coral reefs are not assessed). | |||
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion | Yes – the pressure has a Medium-high risk profile for demersal trawls and seines, and a low risk profile for anchored nets/lines (it is not relevant for pelagic fishing) AND the habitat features have either high sensitivity (Coral gardens, Deep-sea sponge aggregations, Offshore deep-sea muds, Offshore sands and gravels, and Seamount communities) or medium sensitivity (Burrowed mud) to this pressure (mobile species features and Cold-water coral reefs are not assessed) | |||
Changes in suspended solids (water clarity) | Yes – the pressure has a Medium-high risk profile for demersal trawls and seines activities (although it is not relevant for pelagic fishing or anchored nets/lines), AND Coral gardens, Seamount communities and Deep-sea sponge aggregations are sensitive, and Burrowed mud has low sensitivity to this pressure. Cold-water coral reefs, Round-nose grenadier, Leafscale gulper shark/Gulper shark and Portuguese dogfish are not assessed, Offshore deep-sea muds and Offshore sands and gravels are not exposed, and Orange roughy and Blue ling are not sensitive. | |||
Smothering and siltation rate changes (Light) | Yes – the pressure has a Medium-high risk profile for demersal trawls and seines activities (although it is not relevant for pelagic fishing or anchored nets/lines), AND the protected habitat features have either high (Coral gardens, Deep-sea sponge aggregations, Offshore deep-sea muds, Offshore sands and gravels, and Seamount communities) or low sensitivity (Burrowed mud). Cold-water coral reefs and mobile species features are not assessed. | |||
Litter | No - low risk profile for activities (protected feature sensitivity is not assessed) | |||
Underwater noise changes | No – although Coral gardens, Deep-sea sponge aggregations and Seamount communities are sensitive, there is a low risk profile for activities. (Orange roughy, Blue ling, Burrowed mud, Offshore deep-sea muds, and Offshore sands and gravels are not sensitive, and the other features are not assessed). | |||
Introduction of light | No – sensitivity of all protected features is not assessed but there is a low risk profile for activities | |||
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g. boats, machinery and structures) | No – sensitivity of all protected features is not assessed but there is a low risk profile for activities | |||
Visual disturbance | No – sensitivity of all protected features is not assessed but there is a low risk profile for activities | |||
Introduction or spread of invasive non-indigenous species (INIS) | No – sensitivity of protected features is not assessed (except Offshore sands and gravels which is Not sensitive), but there is a low risk profile for activities. | |||
Removal of target species | Yes – the pressure has a Medium-high risk profile AND Orange roughy and Blue ling have high sensitivity, and Burrowed mud has Medium sensitivity (all other protected features are either not assessed or not exposed). | |||
Removal of non-target species | Yes – the pressure has a Medium-high risk profile AND Coral gardens, Deep-sea sponge aggregations, Offshore deep-sea muds, Offshore sands and gravels and Seamount communities have high sensitivity, Burrowed mud and Blue ling have Medium sensitivity, and Orange roughy has low sensitivity (all other protected features are either not assessed or not exposed). |
2.5 Part A conclusion
Considering the information on pressures and sensitivity above demersal trawls, demersal seines, pelagic fishing and anchored nets/lines have the potential to affect the Burrowed mud (including Sea-pens); Coral gardens; Cold-water coral reefs (including Lophelia pertusa reefs); Deep-sea sponge aggregations; Offshore deep-sea muds; Offshore sands and gravels; Seamount communities; Blue ling (Molva dypterygia); Leafscale gulper shark (Centrophorus squamosus) / Gulper shark (Centrophorus granulosus); Orange roughy (Hoplostethus atlanticus); Portuguese dogfish (Centroscymnus coelolepis) and Round-nose grenadier (Coryphaenoides rupestris) within West of Scotland NCMPA through abrasion/disturbance of the substrate on the surface of the seabed; penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion; changes in suspended solids (water clarity); removal of non-target species; removal of target species; and smothering and siltation rate changes (light). These six pressures are considered to affect the features and are taken through to Part B of the assessment.
Contact
Email: marine_biodiversity@gov.scot
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