North-east Lewis Marine Protected Area: business and regulatory impact assessment
An assessment of the business and regulatory impacts of designating the North-east Lewis Marine Protected Area.
Consultation
Within Government
Consultation has been undertaken with policy colleagues within Marine Scotland, including aquaculture, nature conservation, marine renewables, fisheries and fresh water fisheries.
Public Consultation
A stakeholder workshop took place during the development of the underpinning Sustainability Appraisal.
A public consultation ran from 07 June 2019 to 30 August 2019 and included 14 local information events. Consultation responses and feedback from events have been used to finalise the proposals. No changes have been made to the North-east Lewis proposal as a result of responses received.
Options
Option 1 - Do nothing
Option 1 is the 'Do nothing' option; this is the baseline scenario. Under this option, there is no designation at the North-east Lewis pMPA.
Option 2: Designate site as a Nature Conservation Marine Protected Area
Option 2 involves the formal designation of North-east Lewis. Designation would provide recognition and protection to the natural features of the site while also contributing to the national and international MPA networks.
Sectors and groups affected
The following activities have been identified as present (or possibly present in the future) within the proposed North-east Lewis MPA site and potentially interact with one or more of the features:
- Finfish Aquaculture
- Shellfish Aquaculture
- Coastal Protection
- Commercial Fisheries
- Ports and Harbours
- Power Interconnectors
- Telecommunication Cables
Affected sectors may be impacted to a greater or lesser degree by designation depending on which scenario is pursued and which management option is preferred. While the above sectors are all potentially operational within the site, not all will necessarily be impacted by designation and management measures.
Benefits
Option 1: Do nothing
No additional benefits are expected to arise from this policy option.
Option 2: Designate site as a Marine Protected Area
Designation will help to conserve the range of biodiversity in Scottish waters. It will complement other types of designation and provide an essential contribution to establishing an ecologically coherent network of MPAs. This would also safeguard the ecosystem services and benefits provided by the marine environment
Appropriate management will reduce the risk that the extent, population, structure, natural environmental quality and processes of features protected will decrease or degrade over time.
Contribution to an Ecologically Coherent MPA network
Scotland's seas support a huge diversity of marine life and habitats, with around 6,500 species of plants and animals, with plenty more to be found in the undiscovered depths of the north and west of Scotland. Our seas account for 61% of UK waters and remain at the forefront of our food and energy needs, through fishing, aquaculture, oil and gas, and new industries such as renewables, as well as recreation activities and ecotourism. It is likely that an MPA network will demonstrate beneficial effects greater than the sum of the benefits from the individual areas.
MPA designation will help to conserve the range of biodiversity in North-east Lewis and for Scotland as a whole, and will contribute to establishing an ecologically coherent network of marine protected areas.
Ecosystem services benefits
Ecosystems are very complex, and it is thought that the more complex an ecosystem is the more resilient it is to change. Therefore, if it is damaged or if a species or habitat is removed from that ecosystem, the chances of survival for those services reduce as the ecosystem becomes weaker. However, by conserving or allowing the species and habitats that make up that ecosystem to recover, we can be more confident of the continuation of the long-term benefits the marine environment provides.
Non-use value of the natural environment is the benefit people get simply from being aware of a diverse and sustainable marine environment even if they do not themselves 'use it'. We take for granted many of the things we read about or watch, such as bright colourful fish, reefs and strange shaped deep sea curiosities, to lose them would be a loss to future generations that will not be able to experience them. Due to the scientific uncertainty involved it is challenging to put a true value on this, but the high quality experience and increasing knowledge of Scotland's seas can be better preserved through measures such as MPAs. It is expected that non-use value will be attained as a result of designation both from the knowledge that the features are receiving adequate protection along with the wider conservation objectives that designation supports.
In the case of North-east Lewis, it is estimated that effective management of protected features may provide wider benefits over and above these non-use values society places on a healthy and productive marine environment.
Annex A summarises the ecosystem benefits that can be derived from designation of North-east Lewis.
Summary of Benefits
While it may not be possible with current levels of research to monetise benefits with a satisfactory degree of rigour, it is clear that many of the benefits relate to aspects of our lives that we take for granted and for which it is good practice and common sense to maintain through protection measures. These benefits include use values, such as recreational use of the marine environment, as well as non-use values, such as the value that people place on simply knowing that something exists, even if they will never see it or use it.
Kenter et al. examined the value of creating a network of marine protected areas in the UK. From the study it is estimated that, in 2019 prices, the total economic valuation of the North-east Lewis site designation is £5.29 million, rising to £6.04 million when designation is accompanied by management measures[1].
Treating marine protected areas as a collection of individual and separate features providing separate ecosystem services potentially ignores any network effects that could occur from a set of MPAs. A number of adjacent marine reserves may demonstrate network effects, i.e. the benefit from the networks may be greater (or less) than the sum of the benefits from the individual MPAs. Kenter et al. estimated total value of non-use benefits of designating all four sites as £28 million in 2019 prices.
Costs
Option 1: Do nothing
This option is not predicted to create any additional costs to the sectors and groups outlined above. However, it should be noted that the societal cost of not designating could be both large and irreversible relative to the current condition of the marine environment. The absence of management measures to conserve the identified features may produce future economic and social costs[2] in terms of increased marine habitat and biodiversity degradation. The option to not designate holds the potential to undermine the overall ecological coherence of the Scottish MPA Network.
Option 2: Designate site as a Marine Protected Area
Costs have been evaluated based on the implementation of potential management measures. Where feasible costs have been quantified, where this has not been possible costs are stated qualitatively. All quantified costs have been discounted in line with HM Treasury guidance using a discount rate of 3.5% to reflect preference for current consumption over future consumption.
Finfish aquaculture
There are currently no finfish aquaculture sites within the North-east Lewis pMPA, with a single finfish aquaculture site located within a 1 km buffer around the site. It is expected that the finfish aquaculture in the North-east Lewis pMPA will expand over the assessment period, and an assumption has been used below that there will be 1 application for new or expanding sites every 10 years in North-east Lewis. It is assumed that the site in the site currently uses acoustic deterrent devices (ADDs), intended to reduce predation by seals.
It is possible that there may be costs incurred as a result of potential future development in the area, with associated impacts on project delays, on consenting and on wider investment opportunities. Possible social impacts may flow from these economic costs; there may be reduced future employment opportunities if additional costs are significant and render development projects economically unviable or if delays arising from designation impact on potential investment opportunities. However, at this stage it is not possible to quantify these potential future impacts.
Economic Impacts arising from the Designation of the pMPA (2019 to 2038) | ||||
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Lower Estimate | Intermediate Estimate | Upper Estimate | ||
Assumptions for impacts |
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Description of quantified one-off impacts – (on-site) |
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Description of quantified recurring impacts – (on-site) |
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Description of non-quantified costs | On-site |
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Off-site |
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Quantified Costs on the Activity of Designation of the Site as an MPA (in £000s) | ||||
Total costs (2019–2038) | 13 | 105 | 157 | |
Average annual costs | 1 | 5 | 8 | |
Present value of total costs (2019–2038) | 9 | 71 | 107 | |
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%. |
Shellfish aquaculture
There are currently no shellfish aquaculture sites within the North-east Lewis pMPA, and no shellfish aquaculture sites within a 1 km buffer around the site. However, there are a number of sites in close proximity (albeit greater than 1 km from the site) and therefore, with the growth of the industry there is potential for shellfish aquaculture in the North-east Lewis pMPA to develop over the assessment period, and an assumption has been used below that there will be 1 application for a new site (or expansion of existing site) every 10 years in North-east Lewis.
Economic Impacts arising from the Designation of the pMPA (2019 to 2038) | ||||
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Lower Estimate | Intermediate Estimate | Upper Estimate | ||
Assumptions for impacts |
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Description of quantified one-off impacts - (on-site) |
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Description of quantified recurring impacts – (on-site) |
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Description of non-quantified impacts | On-site |
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Off-site |
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Quantified Costs on the Activity of Designation of the Site as an MPA (in £000s) | ||||
Total costs (2019 to 2038) | 13 | 13 | 13 | |
Average annual costs | 1 | 1 | 1 | |
Present value of total costs (2019 to 2038) | 9 | 9 | 9 | |
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%. |
Coastal protection
The data currently available through the Eurosion database currently identifies no coastal protection assets within the site. However, it is thought that there are some areas of hard defence which are likely to require maintenance, and therefore assumptions made as summarised below.
Economic Impacts arising from the Designation of the pMPA (2019 to 2038) | ||||
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Lower Estimate | Intermediate Estimate | Upper Estimate | ||
Assumptions for impacts |
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Description of quantified one-off impacts - (on-site) |
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Description of quantified recurring impacts – (on-site)* |
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Description of non-quantified impacts | On-site |
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Off-site |
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Quantified Costs on the Activity of Designation of the Site as an MPA (in £000s) | ||||
Total costs (2019–2038) | 22 | 22 | 22 | |
Average annual costs | 1 | 1 | 1 | |
Present value of total costs (2019–2038) | 16 | 16 | 16 | |
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%. |
Commercial fisheries
North-east Lewis pMPA lies within ICES rectangles 45E3, 46E3, 45E4 and 46E4 in ICES Division VIa. Approximately 11,697 tonnes of fish and shellfish were landed from these ICES rectangles per annum (2012-2016), predominantly (over 60%) pelagic species by weight and shellfish species (over 50%) by value. The main gear types were midwater and demersal trawls.
VMS-based estimates and ICES rectangle landings statistics indicate that demersal trawls and creels (over-12m vessels) and demersal trawls and creels (under-12m vessels) are the main gear types that operate within the North-east Lewis pMPA. The value of landings from the pMPA was £1.7 million (over-12m vessels, from VMS data) and £4.0 million (under-12m vessels, indicated from ICES rectangle landings data) (annual average for 2012–2016, 2019 prices). Vessels fishing in the North-east Lewis pMPA predominantly operate from: Stornoway and Ullapool (over-12m vessels) and Stornoway and Ayr (under-12m vessels). Landings from the over-12m vessels were made predominantly into Stornoway (50%), Ullapool (28%) and Kinlochbervie (8 %). Landings from the under-12m vessels were made predominantly into Back (27%), Bernera (Lewis) (16%), Stornoway (15%) and Carloway (14%).
For the over-12m vessels, creels operated in particular in the sandeel grounds in the north of the pMPA while demersal trawls operated mainly in the southern part of the pMPA. For the under-12m vessels, creels operated in particular along the coast of Lewis and the southern part of the site.
Due to the small number of vessels operating in the site (less than 5), the value of the loss of fishing income and potential GVA impacts cannot be disclosed for data protection and commercial sensitivity reasons. These values are negligible however.
Economic Impacts arising from the Management Scenarios for the pMPA (2019 to 2038) | ||||
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Lower Estimate | Intermediate Estimate | Upper Estimate | ||
Assumptions for impacts |
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One-off impacts (on-site) |
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Recurring impacts – cost impacts per fleet segment (annual values, £000s, 2019 prices) (on-site)* | Over-12m vessels |
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No gears affected | 0.0 | 0.0 | 0.0 | |
Subtotal over-12m | 0.0 | 0.0 | 0.0 | |
Under-12m vessels |
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Set nets and drift nets | 0.0 | Cannot be disclosed | Cannot be disclosed | |
Subtotal under-12m | 0.0 | Cannot be disclosed | Cannot be disclosed | |
Total all vessels | 0.0 | Cannot be disclosed | Cannot be disclosed | |
Description of non-quantified impacts | On-site |
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Off-site |
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If activity is displaced rather than lost, there is potential for:
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If activity is displaced rather than lost, there is potential for:
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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, which more accurately reflects the wider value of the sector to the local area and economy beyond the market value of the landed catch.[3] Costs are presented in terms of the reduction in full-time equivalent (FTE) employment. It is also possible that effort not continuing in the area could be transferred to other locations resulting in no or reduced loss of income. However, as above, values cannot be disclosed in the intermediate and upper scenarios, as it represents the activity of fewer than 5 vessels.
Quantified Costs on the Activity arising from the Management Scenarios for the MPA (£Million) | |||
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Lower | Intermediate | Upper | |
Total change in GVA (2019–2038) | 0 | Disclosure threshold not met | Disclosure threshold not met |
Average annual change to GVA | 0 | Disclosure threshold not met | Disclosure threshold not met |
Present value of total change in GVA (2019–2038) | 0 | Disclosure threshold not met | Disclosure threshold not met |
Direct and Indirect reduction in Employment | 0 | Disclosure threshold not met | Disclosure threshold not met |
Ports and harbours
There are 5 minor ports and harbours within North-east Lewis pMPA or within a 1 km buffer of the North-east Lewis pMPA (Back, Bayble, Brevig, Garrabost and Ness). Therefore, management costs may be incurred under the assumption that minor ports/harbours will undertake development every 20 years (starting in 2029) within the assessment period (2019-2038).
It should be noted that additional cost impacts could arise as a result of consenting delays. The cost impacts and uncertainty associated with MPA designation may affect investor confidence.
Economic Impacts arising from Designation of the pMPA (2019 to 2038) | |||
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Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for impacts |
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Description of quantified one-off impacts – (on-site) |
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Description of quantified recurring impacts – (on-site) |
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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 (in £000s) | |||
Total costs (2019–2038) | 38 | 38 | 38 |
Average annual costs | 2 | 2 | 2 |
Present value of total costs (2019–2038) | 27 | 27 | 27 |
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%. |
Power interconnectors
There are no power interconnectors currently located within the North-east Lewis pMPA. There is one project identified for potential development over the assessment period (Western Isles HVDC, potentially due for construction in 2021) which crosses the site. This project will require additional assessments to support planning applications (including marine licence) and regular survey to support operation and maintenance following construction.
Economic Impacts arising from the Designation of the pMPA (2019 to 2038) | ||||
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Lower Estimate | Intermediate Estimate | Upper Estimate | ||
Assumptions for impacts |
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Description of quantified one-off impacts – (on-site) |
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Description of quantified recurring impacts – (on-site) |
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Description of non-quantified costs | On-site |
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Off-site |
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Quantified Costs on the Activity of Designation of the Site as an MPA (in £000s) | ||||
Total costs (2019–2038) | 6 | 6 | 686 | |
Average annual costs | 0 | 0 | 34 | |
Present value of total costs (2019–2038) | 6 | 6 | 478 | |
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%. |
Telecommunication cables
There is one telecommunication cable which transits through North-east Lewis (BT-HIE Seg1.13) totalling approximately 15 km of length within the site. This links mainland Scotland with the Isle of Lewis.
Economic Impacts arising from the Designation of the pMPA (2019 to 2038) | |||
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Lower Estimate | Intermediate Estimate | Upper Estimate | |
Assumptions for impacts |
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Description of quantified one-off impacts – (on-site) |
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Description of quantified recurring impacts – (on-site) |
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Description of non-quantified impacts |
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Quantified Costs on the Activity of Designation of the Site as an MPA (in £000s) | |||
Total costs (2019–2038) | 6 | 6 | 6 |
Average annual costs | 0 | 0 | 0 |
Present value of total costs (2019–2038) | 4 | 4 | 4 |
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%. |
Public sector
The decision to designate North-east Lewis as an MPA, would result in costs being incurred by the public sector in the following areas:
- Preparation of Statutory Instruments
- Preparation of a Management Scheme
- Development of voluntary measures
- Site monitoring
- Regulatory and advisory costs associated with licensing decisions
The majority of these costs will accrue at the national level and as such have not been disaggregated to site level. Only the preparation of Statutory Instruments and regulatory and advisory costs associated with licensing decisions have been estimated at the site level
Site-specific Public Sector Costs (£Million, 2019-2038) | |||
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Lower Estimate | Intermediate Estimate | Upper Estimate | |
Preparation of Statutory Instruments | 0 | 0.0042 | 0.0042 |
Preparation of a Management Scheme | 0.0278 | 0.0278 | 0.0278 |
Development of Voluntary Measures | 0.0042 | 0.0042 | 0.0042 |
Site monitoring | 0.324 | 0.324 | 0.324 |
Regulatory costs | 0.007 | 0.007 | 0.007 |
Total Quantified Public Sector Costs | 0.363 | 0.367 | 0.367 |
Average annual costs | 0.018 | 0.018 | 0.018 |
Present value of total costs (2019 to 2038) | 0.274 | 0.278 | 0.278 |
Total costs
Total quantified costs are presented in present value terms. Commercial fisheries costs are presented in terms of GVA.
Total Present Value of Quantified Costs (£Million, 2019-2038) | |||
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Lower Estimate | Intermediate Estimate | Upper Estimate | |
Finfish Aquaculture | 0.009 | 0.071 | 0.107 |
Shellfish Aquaculture | 0.009 | 0.009 | 0.009 |
Coastal Protection | 0.016 | 0.016 | 0.016 |
Ports and Harbours | 0.027 | 0.027 | 0.027 |
Power Interconnectors | 0.006 | 0.006 | 0.478 |
Telecommunication Cables | 0.004 | 0.004 | 0.004 |
Total present value | 0.072 | 0.134 | 0.642 |
GVA Impacts (£Million 2019-2038) | |||
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Commercial Fisheries | 0 | Cannot be disclosed | Cannot be disclosed |
Total Non-Quantified Costs | |||
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Scenario | Lower | Intermediate | Upper |
Sector/Group | |||
Finfish Aquaculture |
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Shellfish Aquaculture |
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Commercial Fisheries |
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Power Interconnectors |
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Contact
Email: marine_conservation@gov.scot
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