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.
East Caithness Cliffs ( ECC)
Site Area (km 2): 117
Site Summary
Table 1. Summary of Proposed Protected Features, Data Confidence and Conservation Objectives | [ ECC] | ||||
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Proposed protected features | |||||
Biodiversity Features Black guillemot. Geodiversity Features None. Site Description The East Caithness Cliffs MPA proposal is located on the east coast of Caithness and represents important breeding and foraging areas for black guillemots. The proposal boundary mirrors the East Caithness Cliffs SPA, extending 2km out to sea from the cliffs. |
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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 | |||||
Black guillemot | *Lower: 116.93 Intermediate: 116.93 Upper: 116.93 |
Yes (Seabird 2000 census) | Yes | Not known | Conserve (uncertain) |
Geodiversity Features | |||||
N/A | |||||
Key: * Estimated area based on best available data References: Area of Feature: GeMs Confidence in feature presence and extent: SNH (2012b) |
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) | [ ECC] | ||
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Human Activity | Cost Impact on Activity | ||
Lower Estimate (£Million) | Intermediate Estimate (£Million) | Upper Estimate (£Million) | |
Quantified Economic Costs (Discounted) | |||
Military | See national costs | See national costs | See national costs |
Ports and Harbours | 0.019 | 0.019 | 0.019 |
Total Quantified Economic Costs | 0.019 | 0.019 | 0.019 |
Non-Quantified Economic Costs | |||
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. |
Table 2b. Site-Specific Public Sector Costs arising from the Designation and Management of the Site as an MPA (over 2014 to 2033 inclusive) | [ ECC] | ||
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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 | None | None | None |
Preparation of Statutory Instruments | None | None | None |
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 | 0.002 | 0.002 | 0.002 |
Total Quantified Public Sector Costs | 0.002 | 0.002 | 0.002 |
Non-Quantified Public Sector Costs | |||
None identified. |
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) | [ ECC] | |||||||||
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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 | |||
No social impacts are expected. |
Table 2d. Site-Specific Benefits arising from the Designation and Management of the Site as an MPA (over 2014 to 2033 inclusive) | [ ECC] | |
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Benefit | Description | |
Ecosystem Services Benefits (Moderate and High Benefits) | Relevance | Scale of Benefits |
Non-use value of natural environment | Low | Low - 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 | [ ECC] | ||||||||||||||||
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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 | |||||||||||||||||
Black guillemot | - | - | - | - | - | - | 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 | |||||||||||||||||
N/A | |||||||||||||||||
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 4a. Military | [ ECC] | ||
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Three military practice areas (Wick (X5819) rifle area; and two firing and danger areas (Tain firing and bombing range and X5819)) overlap with the Black Guillemot feature of the ECC 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 4b. Ports and Harbours | [ ECC] | ||
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There are four ports/harbours (Whaligoe, Dunbeath, Latheronwheel and Lybster) within the ECC proposed MPA boundary. All four ports/harbours overlaps the MPA feature black guillemot 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. | |||
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) | 0.027 | 0.027 | 0.027 |
Average annual costs | 0.001 | 0.001 | 0.001 |
Present value of total costs (2014-2033) | 0.019 | 0.019 | 0.019 |
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
Table 6. Human Activities that are Present but which would be Unaffected by Designation of the Site as an MPA [ ECC] | |
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Activity | Description |
Commercial Fisheries | Dredges and otter trawls (over-15m) and pots, nephrops trawls, other trawls, dredges and other gears (under-15m vessel) operate within the ECC proposed MPA. The value of landings from the ECC area was £26,600 (over-15m vessels) and £98,400 (under-15m vessels, indicated from ICES rectangle landings data) (annual average for 2007-2011, 2012 prices). Landings from the over-15m vessels are into Wick (79% by value), Macduff (7%) and Fraserburgh (6%). VMS data indicate that there are no non- UK vessels fishing within the ECC proposed MPA. Provisional ScotMap data indicate that the annual average earnings from the ECC proposed MPA was £292,700, with over 90% from pots (predominantly for brown crab). The coverage for ScotMap interviews in the region was 66.4% (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. Black guillemot, the proposed designated biodiversity feature for the site, are not thought to be sensitive or vulnerable to pressures from fishing gears, therefore no management measures for fisheries are proposed and no cost impacts are anticipated. |
Oil and Gas | Within the ECC proposed MPA, there are a number of overlaps with oil and gas activity and the extents of features proposed for designation. Under all scenarios, seven wells overlap with the feature extent for the 'black guillemot' within the 1km buffer zone, as well as two licensed blocks and one hydrocarbon field; the Lybster oil field. However, no oil and gas infrastructure is located within the proposed MPA - extraction from the Lybster oil field occurs on land. SNH currently advise that there are no activities currently considered to be a risk to black guillemot within the ECC proposed MPA, and it is unlikely that the MPA would lead to management over and above that already required for the SPA on land. |
Power Interconnectors | One consented power interconnector (Caithness-Moray HVDC Reinforcement) overlaps with the ECC proposed MPA. The power interconnector overlaps with Black Guillemot (all scenarios). No cost impacts are foreseen, as it is assumed that there will be no review of the existing consents. |
Recreational Boating | There are four cruising routes that intersect the ECC proposed MPA boundary; all of which are medium traffic routes. All routes overlap with the lower, intermediate and upper scenarios of the feature extents for black guillemot, although cruising routes are not expected to require additional management measures. Two Crown Estate moorings are present within the proposed MPA that overlap with black guillemot, although black guillemot are not considered sensitive to pressures associated with anchoring, and no costs are expected. |
Social and Distributional Analysis of Impacts from Designation of the Site as an MPA
Table 7a. Social Impacts Associated with Quantified and Non-Quantified Economic Costs | [ ECC] | ||||
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Sector | Potential Economic Impacts | Economic Costs and GVA ( PV) | Area of Social Impact Affected | Mitigation | Significance of Social impact |
None identified. | |||||
Impacts: xxx - significant negative effect; xx - possible negative effects; x - minimal negative effect, if any; 0 - no noticeable effect expected. |
Table 7b. Distribution of Quantified Economic Costs for Commercial Fisheries and Fish Processors (assuming zero displacement of fishing activity) - Location, Age and Gender | [ ECC] | |||||||
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Sector/Impact | Location | Age | Gender | |||||
Region | Ports | Rural, Urban, Coastal or Island | Children | Working Age | Pensionable Age | Male | Female | |
None identified. | ||||||||
Impacts: xxx - significant negative effect; xx - possible negative effects; x - minimal negative effect, if any; 0 - no noticeable effect expected. |
Table 7c. Distribution of Quantified Economic Costs for Commercial Fisheries and Fish Processors (assuming zero displacement of fishing activity) - Fishing Groups, Income Groups and Social Groups | [ ECC] | |||||||
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Sector/Impact | Fishing Groups | Income Groups | Social Groups | |||||
Vessel Category <15m >15m | Gear Types/Sector | 10% Most Deprived | Middle 80% | 10% Most Affluent | Crofters | Ethnic minorities | With Disability or Long-term Sick | |
None identified. | ||||||||
Impacts: xxx - significant negative effect; xx - possible negative effects; x - minimal negative effect, if any; 0 - no noticeable effect expected. |
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 | [ ECC] | ||||
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Feature Name | Representation | Replication | Linkages | Geographic Range and Variation |
Resilience |
Black guillemot | Provides representation of black guillemot in OSPAR Region II. | One of six potential MPAs recommended for black guillemot. | Not currently understood for black guillemot. | Represents the only significant colony on the Scottish east coast. The recommended MPA areas would reflect the geographic range and variation of black guillemot and the environments in which they are present. | Although not listed by OSPAR as threatened and/or declining, there is evidence of decline. The potential MPA areas 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 [2] | [ ECC] | |||||||
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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 | Nil | Nil | Nil | Low. Site fishing grounds have low value | Nil | High |
Fish for non-human consumption | Stocks reduced from potential maximum | Nil | Nil | Nil | ||||
Gas and climate regulation | Nil | Nil | Nil | Nil | Nil | Moderate | Nil | High |
Natural hazard protection | Minimal | Low | Nil | Low | Nil | High | ||
Regulation of pollution | Minimal | Low | Nil | Nil | Low - Moderate, for recreational use of waters | Nil | High | |
Non-use value of natural environment | Low - protected feature, and contribution of the site to MPA network, have non-use value. | Non-use value of the site may decline, but probably stable | Nil, no change in key characteristics of site | Low - protection of feature of site from minor decline | Moderate - protection of feature of site from decline, possibly allowing some recovery | Low, Although black guillemot is charismatic species, it is site's only feature | Low - Moderate | Moderate |
Recreation | Low | 1 active dive site | Nil | Minimal - slightly higher biodiversity encountered by divers and boating | Low | Minimal | Moderate | |
Research and Education | Minimal | Nil - Low | Nil | Minimal | Low | Minimal | Moderate | |
Total value of changes in ecosystem services | Nil for lower scenario, Minimal for upper scenarios | Low | Moderate |
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