Draft Fisheries Assessment – Firth of Forth Banks Complex 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 Firth of Forth Banks Complex 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 impacting 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 impacting the protected features 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:

1. The pressure-feature interactions were not included for Part B:

a. If the feature is not exposed to the pressure, and is not likely to be in the future; or

b. If the effect/impact of the pressure is non-existent or insignificant.

2. The pressure-feature interactions were included for assessment in Part B:

a. If the feature is exposed to the pressure, or is it likely to be in the future; and

b. If the pressure is capable of impacting the feature; or

c. If it is not possible to determine whether pressure is capable of impacting the feature.

Part B of the assessment considers the potential for activities to impact the feature by assessing the impact of fishing gears identified in Part A. This involves determining the 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 Conservation Advice package and Management Options Paper

for Firth of Forth Banks Complex NCMPA have been used to inform this assessment. This is the most recent assessment package and options paper available.

Where appropriate, this advice has been supplemented by information on feature sensitivity from Feature Activity Sensitivity Tool (FeAST) and pressures associated with fishing activity identified from the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022.

2.2 Activities taking place within Firth of Forth Banks Complex NCMPA

To screen out fishing activities that were not taking place within the site or likely to take part on the future, vessel monitoring System (VMS) data within Firth of Forth Banks Complex 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.

Table 1. Gear types recorded from the site based on VMS data from 2015 – 2019.
Gear type Specific gear type Gear code Aggregated gear method
Towed Bottom otter trawl OTB Demersal trawls
Multi-rig trawls OTT
Nephrops trawl TBN
Scottish fly/seine SSC Demersal seine
Dredges Boat dredges (towed) DRB Dredge
Hydraulic dredging Mechanised dredges HMD
Traps Pots/creels FPO Traps/ creels
Towed (pelagic) Mid-water trawl (single) OTM Pelagic fishing

Although pelagic trawling fishing occurs within the site, this is not considered capable of impacting the protected features as this fishing activity does not have contact with the seabed and is therefore not considered further in this assessment.

2.3 Potential pressures exerted by site fishing activity

According to the JNCC Firth of Forth Banks Complex NCMPA Management Option Paper (2014), the fishing activities considered capable of impacting the protected features are demersal seine netting (minimal activity), otter trawling, scallop dredging and creeling and potting. Pelagic trawling and purse seining are activities not considered to be capable of impacting the protected features.

The potential pressures that could be exerted by fishing activities occurring within the site (demersal trawls, demersal seines, dredges and Traps/creels) were determined using the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022. The potential pressures that could be exerted by these gear types are summarised in Table 2.

Table 2. Potential pressures from the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022 and their risk profiling of pressures score, based on the general risk the pressures pose to the environment under normal conditions. Pressures are considered to pose a medium/high risk (dark blue), low risk (light blue), or are not relevant to the activity (white).
PAD pressure Fishing activity
Demersal seine Demersal trawl Dredge Traps/ creels
Above water noise Low Low Low Low
Abrasion/disturbance of the substrate on the surface of the seabed Medium-high Medium-high Medium-high Medium-high
Barrier to species movement Not relevant Not relevant Not relevant Not relevant
Changes in suspended solids (water clarity) Medium-high Medium-high Medium-high Not relevant
Collision ABOVE water with static or moving objects not naturally found in the marine environment (e.g., boats, machinery, and structures) Low Low 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
Deoxygenation Low Low Low Low
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. Low Low Low Low
Introduction of light Low Low Low Low
Introduction of microbial pathogens Low Low Low Low
Introduction or spread of invasive non-indigenous species (INIS) Low Low Low Low
Litter Low Low Low Low
Nutrient enrichment Low Low Low Not relevant
Organic enrichment Low Low Low Low
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion Medium-high Medium-high Medium-high Low
Physical change (to another seabed type) Low Low Low Not relevant
Physical change (to another sediment type) Low Low Low Not relevant
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
Smothering and siltation rate changes (Light) Medium-high Medium-high Medium-high Not relevant
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. Low Low Low Low
Transition elements and organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC Low Low
Underwater noise changes Low Low Low Low
Visual disturbance Low Low Medium-high Low

2.4 Significance of effects/impacts to protected features

To determine whether each pressure is likely to have a significant effect on the site’s features, the sensitivity assessments and risk profiling of pressures from FeAST and the JNCC Marine Pressures-Activities Database (PAD) v1.5 2022 were used (Table 3). For the Firth of Forth Banks Complex NCMPA, following JNCC advice, FeAST was used to establish the feature sensitivity to the relevant pressures for Ocean Quahog aggregation and Offshore subtidal sands and gravels feature. This was to ensure the most up to date sensitivity evidence was used.

As offshore subtidal sands and gravels are not a feature assessed within FeAST, continental shelf mixed sediments, continental shelf coarse sediments and continental shelf sands were used as comparable habitat. This decision was informed by the Data confidence assessment undertaken for the NCMPA which utilised predictive habitat map, EUSeaMap[1]. This was used to indicate extent of supporting habitats within the site. The map is the result of work undertaken by a consortium lead by the JNCC to combine physical data describing the marine environment with information from biological sampling, generating a broad-scale habitat model of seabed habitats from which a predictive map was created (Cameron & Askew, 2011).

The habitat map from the model predicts offshore subtidal sands and gravels occur across the entire MPA. A5.14 Circalittoral coarse sediment, A5.15 Deep circalittoral coarse sediment, A5.25 Circalittoral fine sand or A5.26 Circalittoral muddy sand and A5.27 Deep circalittoral sand are predicted to occur in each of the three parts of the Firth of Forth Banks Complex NCMPA, the latter being the most dominant sediment type (comprising ~48% of the MPA). A small patch (<1% of the MPA) of A5.45 Deep circalittoral mixed sediments is predicted to occur in the Montrose Bank part and in the western part around Wee Bankie and Scalp Bank. Confidence in the presence and extent of the protected features has been set out in the Data Confidence Assessment.

Table 3 identifies the pressures from particular gears that could be capable of impacting each feature. Where a pressure from a particular gear is identified as being capable of impacting 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 as being capable of impacting a feature but which do interact with the feature are considered in the in-combination aspect of the assessment (Part C). 

Table 3. FeAST sensitivity categorisation for protected features of Firth of Forth Banks Complex NCMPA, showing the pressures from specific activities and the potential sensitivity of the protected features. The features are categorised as being High, Medium or Sensitive (dark blue), Low or Not assessed (light blue), Not Sensitive (white), and Not relevant/exposed (white). Further details on these categories are available in the associated methods document.
Potential pressure Protected feature
Ocean quahog aggregations Offshore subtidal sands and gravels
Continental shelf mixed sediments Continental shelf coarse sediments Continental shelf sands
Above water noise Not relevant Not relevant Not relevant Not relevant
Abrasion/disturbance of the substrate on the surface of the seabed Low Medium High Medium
Barrier to species movement Not relevant Not relevant Not relevant Not relevant
Changes in suspended solids (water clarity) Not exposed Medium Not sensitive Not sensitive
Collision ABOVE water with static or moving objects not naturally found in the marine environment (e.g., boats, machinery, and structures) Not relevant Not relevant Not relevant Not relevant
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g. boats, machinery and structures) Not relevant Not relevant Not relevant Not relevant
Deoxygenation Not sensitive Not exposed Not exposed Not exposed
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. Sensitive Sensitive Sensitive Sensitive
Introduction of light Not relevant Not relevant Not relevant Not relevant
Introduction of microbial pathogens Not assessed Not assessed Not assessed Not assessed
Introduction or spread of invasive non-indigenous species (INIS) Not assessed High Medium Medium
Litter Not assessed Not assessed Not assessed Not assessed
Nutrient enrichment Not assessed Not sensitive Not sensitive Not sensitive
Organic enrichment Not sensitive Not sensitive Not sensitive Not sensitive
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion High High Medium Medium
Physical change (to another seabed/sediment type) High High Medium High
Removal of target species Not exposed Not exposed Not exposed Not exposed
Removal of non-target species Medium Medium Medium Medium
Smothering and siltation rate changes (Light) Not sensitive Not sensitive Medium Medium
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. Sensitive Sensitive Sensitive Sensitive
Transition elements and organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC Sensitive Sensitive Sensitive Sensitive
Underwater noise changes Not sensitive Not sensitive Not sensitive Not sensitive
Visual disturbance Not relevant Not relevant Not relevant Not relevant

Considering both the information on pressure activity association (Table 2) and the sensitivity of the features (Table 3), pressures that have the potential to impact the feature are summarised in Table 4.

Pressures that are not exerted by the fishing activity within the site are identified as ‘not relevant to the activity’ in Table 4 and 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 case 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.

Pressures from the FeAST sensitivity assessment for the relevant features that were not sensitive, not exposed, not relevant or unknown were not considered further in the assessment (Table 4).

Of all the pressures considered, five with a medium-high risk profile (PAD) also have a medium high sensitivity for the protected features. These are abrasion/disturbance of the substrate on the surface of the seabed; changes in suspended solids (water clarity), penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion, smothering and siltation rate changes (light) and removal of non-target species. These five pressures are subsequently considered to have the potential to impact the protected features. All five of these pressures are exerted by demersal trawls, demersal seines and dredges. Abrasion/disturbance of the substrate on the surface of the seabed is also exerted by traps/creels activity.

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 as capable of impacting the feature but which do interact with the features are considered in the in-combination aspect of the assessment (Part C).

Table 4 Summary of pressures that could be capable of impacting the protected features, based on pressure-activity associations and sensitivity. Pressures that are capable of impacting are in dark blue.
Potential Pressure Fishing activity
Demersal Seine Demersal trawl Dredges Traps/creels
Above water noise No - Pressure not relevant to activity or features
Abrasion/disturbance of the substrate on the surface of the seabed Yes - Medium-high and continental shelf mixed sediments sensitive
Barrier to species movement No - Pressure not relevant to activity
Changes in suspended solids (water clarity) Yes - Medium-high risk of pressure from activity and continental shelf mixed sediments sensitive Pressure not relevant to activity
Collision ABOVE water with static or moving objects not naturally found in the marine environment (e.g., boats, machinery, and structures) No - Low risk of pressure from activity and not relevant to features
Collision BELOW water with static or moving objects not naturally found in the marine environment (e.g. boats, machinery and structures) No - Low risk of pressure from activity and not relevant to features
Deoxygenation No - Low risk of pressure from activity and either not relevant to features or features not sensitive
Hydrocarbon & PAH contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC. No - Features are sensitive but low risk of pressure from activity
Introduction of light No - Low risk of pressure from activity and not relevant to features
Introduction of microbial pathogens No - Low risk of pressure from activity though feature sensitivity is not assessed for boat dredge and hydraulic dredge
Introduction or spread of invasive non-indigenous species (INIS) No - Low risk of pressure from activity though ocean quahog are not assessed and offshore sands and gravels are sensitive
Litter No - Low risk of pressure from activity though features are not assessed
Nutrient enrichment No - Low risk, or pressure not relevant to activity and features are not sensitive or not assessed
Organic enrichment No - Low risk of pressure from activity and features not sensitive
Penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion Yes – Medium-high risk of pressure from activity and features are sensitive No - low risk of pressure from activity
Physical change (to another seabed/sediment type) No - Low risk, or pressure not relevant to activity though features are sensitive
Removal of target species No – Medium-high risk of pressure from activities however pressure is not relevant to the features
Removal of non-target species Yes - Medium-high risk of pressure from activities and features are sensitive No – not relevant to activity
Smothering and siltation rate changes (Light) Yes - Medium-high risk of pressure from activities and two components of offshore No – not relevant to activity
Synthetic compound contamination (incl. pesticides, antifoulants, pharmaceuticals). Includes those priority substances listed in Annex II of Directive 2008/105/EC. No - Features are sensitive but low risk of pressure from activity
Transition elements and organo-metal (e.g. TBT) contamination. Includes those priority substances listed in Annex II of Directive 2008/105/EC No - Features are sensitive but low risk of pressure from activity
Underwater noise changes No - Low risk of pressure from activity and features not sensitive
Visual disturbance No - Low risk of pressure from activity and pressure not relevant to features No – Although Medium-high risk of pressure from activities, the pressure is not relevant to the features No - Low risk of pressure from activity and pressure not relevant to features

2.5 Part A Conclusion

Considering the information on pressures and sensitivity above, demersal trawls, demersal seines, dredge or traps/creels have the potential to impact offshore subtidal ands and gravels or ocean quahog aggregations features of Firth of Forth Banks Complex NCMPA, through abrasion/disturbance of the substrate on the surface of the seabed; changes in suspended solids (water clarity), penetration and/or disturbance of the substrate below the surface of the seabed, including abrasion; smothering and siltation (light) and removal of non-target species. The only pressure associated with traps/creels was abrasion/disturbance of the substrate on the surface of the seabed. The five pressures are considered to have the potential to impact the features are taken through to Part B of the assessment.

Contact

Email: marine_biodiversity@gov.scot

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