Planning Scotland's Seas: 2013 - The Scottish Marine Protected Area Project – Developing the Evidence Base for Impact Assessments and the Sustainability Appraisal Final Report - Appendix E - Marine Site Reports
This is Appendix E for the pMPA Impact and Sustainability Report containing the detailed site by site reports. Published separately due to size.
Loch Sunart to the Sound of Jura ( SJU)
Site Area (km 2): 795
Site Summary
Table 1. Summary of Proposed Protected Features, Data Confidence and Conservation Objectives | [ SJU] | ||||
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Proposed protected features | |||||
Biodiversity Features Common skate. Geodiversity Features Quaternary of Scotland - glaciated channels/troughs (other features to be confirmed by SNH). Site Description The Loch Sunart to the Sound of Jura MPA proposal extends northwards from the Sound of Jura, covering the Firth of Lorn and the south-western part of Loch Linnhe. The proposal site extends through the Sound of Mull and into Loch Sunart. |
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Summary of confidence in presence, extent and condition of proposed protected features and conservation objectives | |||||
Proposed Protected Feature | Estimated Area of Feature (by scenario) (km 2) | Confidence in Feature Presence |
Confidence in Feature Extent |
Confidence in Feature Condition |
Conservation Objective and Risk |
Biodiversity Features | |||||
Common skate | *Lower: 795.04 Intermediate: 795.04 Upper: 795.04 |
Yes (Marine Scotland Science trawl data, 1975 - present; MSS tagging, 2011 - 2013) | Yes | Not known | Conserve |
Geodiversity Features | |||||
Quaternary of Scotland - glaciated channels/troughs (other features to be confirmed by SNH) | 87.74 | Yes (Nature conservation work) | Partial - need to define additional components | Not known | Conserve |
Key: * Estimated area based on best available data References: Area of Feature: GeMs Confidence in feature presence and extent: SNH (2012g) |
Summary of Costs and Benefits
Table 2a. Site-Specific Economic Costs on Human Activities arising from the Designation and Management of the Site as an MPA (present value of total costs over 2014 to 2033 inclusive) | [ SJU] | ||
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Human Activity | Cost Impact on Activity | ||
Lower Estimate (£Million) | Intermediate Estimate (£Million) | Upper Estimate (£Million) | |
Quantified Economic Costs (Discounted) | |||
Aquaculture (Finfish) | 0.018 | 0.076 | 0.076 |
Aquaculture (Shellfish) | See national costs | See national costs | See national costs |
Commercial Fisheries* | 0.000 | 1.447 | 3.437 |
Energy Generation | 0.037 | 0.229 | 0.229 |
Military | See national costs | See national costs | See national costs |
Ports and Harbours | 0.053 | 0.053 | 0.053 |
Total Quantified Economic Costs | 0.108 | 1.804 | 3.794 |
Non-Quantified Economic Costs | |||
Aquaculture (Finfish) |
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Aquaculture (Shellfish) |
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Commercial Fisheries |
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Energy Generation |
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Military |
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Ports and Harbours |
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Note: For detailed information on economic cost impacts on activities, see Table 4. * These estimates (present value of total change in GVA) assume zero displacement of fishing activity and hence are likely to overestimate the costs. |
Table 2b. Site-Specific Public Sector Costs arising from the Designation and Management of the Site as an MPA (over 2014 to 2033 inclusive) | [ SJU] | ||
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Description | Public Sector Costs | ||
Lower Estimate (£Million) | Intermediate Estimate (£Million) | Upper Estimate (£Million) | |
Quantified Public Sector Costs (Discounted) | |||
Preparation of Marine Management Schemes | 0.024 | 0.024 | 0.024 |
Preparation of Statutory Instruments | None | 0.004 | 0.004 |
Development of voluntary measures | National assessment | National assessment | National assessment |
Site monitoring | National assessment | National assessment | National assessment |
Compliance and enforcement | National assessment | National assessment | National assessment |
Promotion of public understanding | National assessment | National assessment | National assessment |
Regulatory and advisory costs associated with licensing decisions | 0.009* | 0.009* | 0.009* |
Total Quantified Public Sector Costs | 0.033 | 0.037 | 0.037 |
Non-Quantified Public Sector Costs | |||
None identified. | |||
* Regulatory and advisory costs of finfish and shellfish aquaculture assessed at national level. |
Table 2c. Summary of Social Impacts and Distribution of Quantified Impacts arising from the Designation and Management of the Site as an MPA (over 2014 to 2033 inclusive) | [ SJU] | |||||||||
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Key Areas of Social Impact | Description | Scale of Expected Impact across Scenarios, Average (mean no. of jobs affected) | Distributional Analysis | |||||||
Location | Fishing Groups Predominantly Affected | Social Groups Affected | ||||||||
Region | Port | Rural/ Urban/ Island | Gear Types Most Affected | Vessels most affected | Crofters | Ethnic minorities | With disability or long term sick | |||
Employment with consequent impacts on: Health, Crime, Environment, and Culture and Heritage | Commercial fisheries - Loss of jobs (direct and indirect) | Lower: 0 jobs Intermediate: 3 jobs Upper: 5 jobs |
West West |
Oban Campbeltown |
Impacts concentrated in urban and rural coastal areas | Nephrops trawls Dredges |
Lower: N/A Upper: >15m |
No Impact. | No breakdown of fisherman employment by ethnic origin. | No employment data but unlikely to be employed in fisheries. |
If any energy generation developments do not proceed as a result of designation (due to additional costs, project delays, loss of investor confidence), there may be significant social impacts due to job losses (non-quantified). | ||||||||||
Note: For detailed information on socio-economic impacts by sector, see Table 7a. For more detailed information on distributional impacts of quantified costs by sector see Tables 7b and 7c. |
Table 2d. Site-Specific Benefits arising from the Designation and Management of the Site as an MPA (over 2014 to 2033 inclusive) | [ SJU] | |
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Benefit | Description | |
Ecosystem Services Benefits (Moderate and High Benefits) | Relevance | Scale of Benefits |
Non-use value of natural environment | Moderate. Protected features are endangered species and wrecks, and contribution of the site to MPA network has non-use values. Wrecks are protected by virtue of designation under what are soon to become Historic MPAs. | Minimal - Moderate |
Other Benefits | ||
Tourism | Higher biodiversity due to designation, and presence of designations, may attract more tourism activity to local economy. | |
Contribution to ecologically coherent network | See report Section 7.5. | |
Note: For detailed information on ecosystem services benefits, see Tables 9 and 10. For detailed information on other benefits, see Table 5 (activities that would benefit) and Table 8 (contribution to ecologically-coherent network). |
Summary of Overlaps and Interactions between Proposed Designated Features and Human Activities
Table 3. Overlaps and Potential Interactions between Features and Activities under different Scenarios, indicating need for Assessment of Cost Impacts on Human Activities from Designation of the Site as an MPA | [ SJU] | ||||||||||||||||
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Aggregates | Aquaculture (Finfish) | Aquaculture (Shellfish) | Aviation | Carbon Capture & Storage | Coastal Protection | Commercial Fisheries | Energy Generation | Military Activities | Oil & Gas | Ports & Harbours | Power Interconnectors | Recreational Boating | Shipping | Telecom Cables | Tourism | Water Sports | |
Biodiversity Features | |||||||||||||||||
Common skate | - | L/I/U | L/I/U | - | - | - | L/I/U | L/ I/ U | L/I/U | - | L/ I/ U | L/I/U | L/I/U | - | - | L/I/U | L/I/U |
Geodiversity Features | |||||||||||||||||
Quaternary of Scotland - glaciated channels/troughs (other features to be confirmed by SNH) | Not considered to be sensitive at the levels of exposure expected from human activities; thus, not considered in the context of management. | ||||||||||||||||
Note: L = Lower Scenario; I = Intermediate Scenario; U = Upper Scenario. Normal font indicates that there is an overlap between the activity and proposed designated feature under that scenario, bold indicates that the overlap results in a potential interaction between the activity and proposed designated feature that has resulted in cost impacts under that scenario. For detail of management measures assessed under each scenario for each activity, and results of the cost estimates, see Table 4. |
Human Activity Summaries
Human activities that would be impacted by designation of the site as an MPA
Table 4b. Aquaculture (Shellfish) | [ SJU] | ||
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There are 21 shellfish farms (Acairseid Mhor, Ardfad, Ardshellach, Aros Estuary, Balvicar, Camas Inas, Cutter Rock, East Balvicar, Gigas, Liddesdale, Lismore Seafoods, Melfort, Oitir Mhor Bay, Port Na Coite, Rhuda Aird Beithe, Sgeir Liath, Sgeir Liath - Mhor, Site 1 and Tobermory Bay) within the SJU proposed MPA boundary . All 21 sites directly overlap with the feature Common Skate under all scenarios (lower, intermediate and upper). There are three additional shellfish farms within 1km of the proposed MPA boundary under all sceneraios (Husky, Loch Crinan and Portmor). There is no public information on potential future development within the proposed MPA. In the absence of information on potential future developments, no site specific assessment has been possible. A national assessment of the costs of obtaining planning permission for new developments is provided separately. |
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Economic Costs on the Activity of Designation of the Site as an MPA | |||
Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for cost impacts |
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Description of one-off costs |
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Description of recurring costs |
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Description of non-quantified costs |
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Quantified Costs on the Activity of Designation of the Site as an MPA (£Million) | |||
Total costs (2014-2033) | See national costs | See national costs | See national costs |
Average annual costs | See national costs | See national costs | See national costs |
Present value of total costs (2014-2033) | See national costs | See national costs | See national costs |
Total costs = Sum of one-off costs and recurring costs for the site summed over the 20 year period. Average annual costs = Total costs divided by the total number of years under analysis ( i.e. 20). Present value of total costs = Total costs discounted to their current value, using a discount rate of 3.5%. |
Table 4c. Commercial Fisheries (assuming zero displacement of fishing activity) | [ SJU] | ||
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According to VMS-based estimates and ICES rectangle landings statistics, Dredges, nephrops trawls, whifefish trawls, hand fishing and other gears (over-15m) and pots, nephrops trawls, dredges and other gears (under-15m vessels) operate within the SJU proposed MPA. The value of catches from the SJU area was £710,000 (over-15m vessels) and £490,000 (under-15m vessels, indicated from ICES rectangle landings data) (annual average for 2007-2011, 2012 prices). Landings from the over-15m vessels were predominantly into Oban (51% by value), Crinan (16%) and Cuan (8%). For the over-15m fleet, dredgers and nephrops trawlers operated in particular over the whole proposed MPA and across the common skate feature. Provisional ScotMap data indicate that the annual average earnings from the SJU proposed MPA was £1,153,800, with over 80% of this from pots, and 13% from diving, neither of which are expected to be affected by management measures assessed under the scenarios. The spatial distribution of value from Nephrops trawls indicates that the majority of value from the relevant ICES rectangles (41E4, 42E3 and 42E4) is derived from the area outside the SJU proposed MPA. It is likely that the ICES rectangle estimate for the cost impact on <15m nephrops trawls is an over-estimate. ScotMap data would indicate an annual cost impact of around £0.04 million on <15m Nephrops trawls under the Upper Scenario. Provisional ScotMap data also indicate minimal dredge activity within the SJU area, suggesting that the estimate from ICES rectangle data for dredges is also an over-estimate. The coverage for ScotMap interviews in the region was 63.8% (total value of reported landings from the Fisheries Information Network for those vessels included in the ScotMap value analysis expressed as a percentage of the total reported landings for all vessels <15m). Therefore the ScotMap estimate is likely to under-represent the value of fishing by under-15m vessels, and the spatial representation of the value of fishing is less robust than in regions where coverage is higher. VMS data indicate that there were 4 non- UK vessels within the SJU proposed MPA (3 Irish and 1 Norwegian), but these vessels will not have been actively fishing within the proposed MPA, which is within 6nm, and is more likely to have been transiting the area. Management measures for the scenarios have been developed based on the sensitivity and vulnerability of the features to the pressures caused by different gear types and SNH recommendations. Common skate are distributed throughout the proposed MPA area and although there is no targeted fishery for skate (retention of common skate on board is prohibited), skate may be caught as bycatch in other fisheries. The Clyde Fishermen's Association have indicated that the value of the scallop fishery in the area is likely to be greater than the value indicated for dredges in the Upper scenario and would increase if the Firth of Lome area were to reopen to scallop dredging. Unlike most other sectors, the potential cost of designation on commercial fisheries is a loss or displacement of current (and future) output, caused by restrictions on fishing activities. Any decrease in output will, all else being equal, reduce the Gross Value Added ( GVA) generated by the sector and have knock-on effects on the GVA generated by those industries that supply commercial fishing vessels. The costs estimates for this sector have therefore been estimated in terms of GVA. GVA estimates have been generated by applying fleet segment-specific ' GVA/total income' ratios to the value of landings affected. The GVA ratios have been calculated using data on total income and GVA from the Sea Fish Industry Authority Multi-year Fleet Economic Performance Dataset (published March 2013). Further details on the GVA ratios and the methodology for estimating GVA and employment impacts applied are presented in Appendix C7. It is important to note that all costs presented below assume that all affected landings are lost, that is, there is no displacement of fishing activity to alternative fishing grounds. In reality, some displacement is likely to occur and hence the cost, GVA and employment impacts presented in this table are likely to overestimate the costs. |
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Economic Costs on the Activity of Designation of the Site as an MPA | |||
Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for cost impacts |
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Description of one-off costs |
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Description of recurring costs |
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Description of non-quantified costs |
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Quantified Costs on the Activity of Designation of the Site as an MPA (£Million) | |||
Total costs (2014-2033) | 0.000 | 4.647 | 9.294 |
Average annual costs | 0.000 | 0.232 | 0.465 |
Present value of total costs (2014-2033) | 0.000 | 3.418 | 6.835 |
Economic Impacts(£Million) | |||
Total change in GVA (2014-2033) | 0.000 | 1.967 | 4.673 |
Average annual change to GVA | 0.000 | 0.098 | 0.234 |
Present value of total change in GVA (2014-2033) | 0.000 | 1.447 | 3.437 |
Direct and Indirect reduction in Employment | 0.0 jobs | 2.6 jobs | 5.3 jobs |
Total costs = Sum of one-off costs and recurring costs for the site summed over the 20 year period. Average annual costs = Total costs divided by the total number of years under analysis ( i.e. 20). Present value of total costs = Total costs discounted to their current value, using a discount rate of 3.5%. Total change in GVA (2014-2033) = The change in direct GVA in the sector for the site summed over the 20 year period. Average annual change to GVA = Total change in direct GVA in the sector for the site divided by the total number of years under analysis ( i.e. 20). Present value of total change in GVA (2014-2033) = Total change in direct GVA in the sector for the site discounted to current value, using a discount rate of 3.5%. Direct and Indirect reduction in Employment = The average (mean) reduction in direct employment in the sector plus the indirect reduction in employment on the sector's suppliers |
Table 4d. Energy Generation | [ SJU] | ||
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There are no energy generation activities currently operating within the SJU proposed MPA boundary or corresponding buffer zones. Thus, economic costs and management measures associated with energy generation in this proposed MPA are described in light of known possible future developments. Two possible export cable routes (north and south of the Isle of Mull) for the potential Argyll Array Windfarm (ScottishPower Renewables, project currently on hold, up to 1800 MW capacity) overlap the OSPAR and BAP designated MPA mobile species feature 'Common Skate' under all scenarios. Note, only one of these export cable routes will be chosen upon application. Three potential future export cable routes from offshore wind, wave and tidal energy Areas of Search (AoS) overlap the MPA feature Common Skate extents under all scenarios. Additional assessments of potential impacts to Common Skate feature will be required for all of these potential future developments under all scenarios. While Common Skate may be sensitive to electromagnetic fields ( EMF) associated with live power cables, it has been assumed that no additional mitigation measures would be required beyond existing good practice (burial to 1-2m in sediment habitats). Therefore, no additional mitigation costs would be attributable to the designation of the proposed MPA. However, additional post-licence monitoring costs may be incurred for intermediate and upper scenarios. | |||
Economic Costs on the Activity of Designation of the Site as an MPA | |||
Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for cost impacts |
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Description of one-off costs |
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Description of recurring costs |
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Description of non-quantified costs |
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Quantified Costs on the Activity of Designation of the Site as an MPA (£Million) | |||
Total costs (2014-2033) | 0.048 | 0.348 | 0.348 |
Average annual costs | 0.002 | 0.017 | 0.017 |
Present value of total costs (2014-2033) | 0.037 | 0.229 | 0.229 |
Total costs = Sum of one-off costs and recurring costs for the site summed over the 20 year period. Average annual costs = Total costs divided by the total number of years under analysis ( i.e. 20). Present value of total costs = Total costs discounted to their current value, using a discount rate of 3.5%. |
Table 4e. Military | [ SJU] | ||
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Fifteen military practice areas (Jura Sound (X5623), Linnhe (X5624), Staffa (X5627) and Mull (X5628); and 11 submarine exercise areas) overlap with the feature common skate of the SJU proposed MPA under all scenarios (lower, intermediate and upper). The features and associated habitats which overlap with military activities have not been described as vulnerable to MOD activities in this proposed MPA. It is assumed that management relating to MOD activity will be coordinated through the MOD's Maritime Environmental Sustainability Appraisal Tool ( MESAT) which the MOD uses to assist in meeting its environmental obligations. This process will include operational guidance to reduce significant impacts of military activities on MPAs. It is assumed that the MoD will incur additional costs in adjusting MESAT and other MoD environmental assessment tools in order to consider whether its activities will impact on the conservation objectives of MPAs and also incur additional costs in adjusting electronic charts to consider MPAs. However, these costs will be incurred at national level and hence no site-specific cost assessments have been made. |
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Economic Costs on the Activity of Designation of the Site as an MPA | |||
Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for cost impacts |
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Description of one-off costs | |||
Description of recurring costs | |||
Description of non-quantified costs | |||
Quantified Costs on the Activity of Designation of the Site as an MPA (£Million) | |||
Total costs (2014-2033) | See national costs | See national costs | See national costs |
Average annual costs | See national costs | See national costs | See national costs |
Present value of total costs (2014-2033) | See national costs | See national costs | See national costs |
Total costs = Sum of one-off costs and recurring costs for the site summed over the 20 year period. Average annual costs = Total costs divided by the total number of years under analysis ( i.e. 20). Present value of total costs = Total costs discounted to their current value, using a discount rate of 3.5%. |
Table 4f. Ports and Harbours | SJU | ||
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There are 11 ports/harbours (Ardnamurchan, Balvicar, Cuan, Luing, Oban NLB Base, Oban North Pier, Oban Railway Pier, Salen, Tayvallich, Tobermory and Toberonochy) within the SJU proposed MPA boundary that all overlap with feature extents for common skate under all scenarios. Therefore, management costs may be incurred under the assumption that small ports/harbours will undergo one new development within the relevant time frame (2014-2033), assumed for the year 2024. There are 14 anchorages/mooring areas within the SJU proposed MPA boundary, all of which overlap the feature common skate under all scenarios. |
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Economic Costs on the Activity of Designation of the Site as an MPA | |||
Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for cost impacts |
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Description of one-off costs |
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Description of recurring costs |
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Description of non-quantified costs |
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Quantified Costs on the Activity of Designation of the Site as an MPA (£Million) | |||
Total costs (2014-2033) | 0.074 | 0.074 | 0.074 |
Average annual costs | 0.004 | 0.004 | 0.004 |
Present value of total costs (2014-2033) | 0.053 | 0.053 | 0.053 |
Total costs = Sum of one-off costs and recurring costs for the site summed over the 20 year period. Average annual costs = Total costs divided by the total number of years under analysis ( i.e. 20). Present value of total costs = Total costs discounted to their current value, using a discount rate of 3.5%. |
Human activities that would benefit from designation of the site as an MPA
Human activities that are present but which would be unaffected by designation of the site as an MPA
Social and Distributional Analysis of Impacts from Designation of the Site as an MPA
Potential Contribution of the Site to an Ecologically-Coherent Network
Table 8. Overview of Features Proposed for Designation and how these contribute to an Ecologically Coherent Network of MPAs | [ SJU] | ||||
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Feature Name | Representation | Replication | Linkages | Geographic Range and Variation |
Resilience |
Common skate | Provides representation for the only MPA search area identified for common skate in OSPAR Region III; where large, mature individuals are believed to be resident. | Represents the only area in which common skate have been identified. | Represents the only MPA search area in which common skate are believed to reside. | Listed by OSPAR as threatened and/or declining. The MPA area may increase resilience. | |
JNCC (pers. comm.); SNH and JNCC. (2012). Assessment of the potential adequacy of the Scottish MPA network for MPA search features: summary of the application of the stage 5 selection guidelines. Available online from: http://www.scotland.gov.uk/Topics/marine/marine-environment/mpanetwork/engagement/270612. |
Anticipated Benefits to Ecosystem Services
Table 9. Summary of Ecosystem Services Benefits arising from Designation of the Site as an MPA [6] | [ SJU] | |||||||
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Services | Relevance to Site |
Baseline Level | Estimated Impacts of Designation | Value Weighting | Scale of Benefits | Confidence | ||
Lower | Intermediate | Upper | ||||||
Fish for human consumption | Moderate. Habitats make contribution to food webs. | Stocks not at MSY, Skate endangered | Nil | Low, impact of preventing bycatch on populations of Skate and other species uncertain | Moderate. Common Skate is potentially a commercial species | Nil - Low | Low | |
Fish for non-human consumption | Stocks reduced from potential maximum | |||||||
Gas and climate regulation | Nil - Low | Nil - Low | Nil | Low | Low | Moderate | Nil - Minimal | High |
Natural hazard protection | Low | Low | Nil, would not affect stability of coastline | Low | Nil | High | ||
Regulation of pollution | Low | Low | Nil | Nil - Low, maintained by protecting seabed features | Low - Moderate, for recreational use of waters | Nil - Minimal | High | |
Non-use value of natural environment | Moderate - protected feature is endangered species, wrecks (designated under future Historic MPAs) and contribution of the site to MPA network, have non-use value. | Non-use value of the site may decline | Minimal, no change in key characteristics of site | Low - Moderate, protection of key characteristics of site from decline, and/or allowing some recovery of values | Moderate | Minimal - Moderate | Low | |
Recreation | Moderate | 42 active dive sites, boating anchorages, sea angling | Nil | Low, slightly higher biodiversity encountered by divers and boating | Moderate, important contribution to halting loss of one species | Nil - Low | Moderate | |
Research and Education | Moderate | Biological feature has research value, and has few substitutes | Nil, no change in characteristics of site | Low - Moderate, protection of key characteristics of site from decline, improving future research opportunities | Low | Nil - Low | Low | |
Total value of changes in ecosystem services | Nil for lower scenario, Low - Moderate for upper scenario | Nil - Low | Low |
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