Item 11 Appendix 3: Nature Scot Comments Clune Windfarm 20250047PAC
Cairngorms National Park Authority Ughdarras Pairc Nàiseanta a’ Mhonaidh Ruaidh
Agenda item 11
Appendix 3
2025/0047/PAC (ECU00005038)
NatureScot comments
Item 11 Appendix 3 29 August 2025 Page 1 of 23
NatureScot NadarAlba Scotland’s Nature Agency Buidheann Nàdair na h‑Alba
Rebecca Hindson Energy Consents Unit Response by email to [email protected]
27 June 2025 Your ref: ECU00005038 Our ref: CDM179372
Dear Rebecca Hindson
ELECTRICITY ACT 1989 THE ELECTRICITY WORKS (ENVIRONMENTAL IMPACT ASSESSMENT) (SCOTLAND) REGULATIONS 2017 APPLICATION FOR SECTION 36 CONSENT FOR CLUNE WIND FARM
Thank you for your consultation on the above proposal dated 20 February 2025 and for allowing us additional time to respond.
Summary
This proposal will have significant adverse effects on the special qualities of the Cairngorms National Park such that the objectives of the designation and overall integrity of the area would be compromised. We therefore object to this proposal. River Spey Special Area of Conservation (SAC): The proposal could affect internationally important natural heritage interests and we therefore object to this proposal until further information is provided. This will enable us to carry out an appraisal of these effects and help you determine this proposal. Kinveachy Forest Site of Special Scientific Interest (SSSI): The proposal could affect nationally important natural heritage interests and we therefore object to this proposal until further information is provided. White-tailed eagle: We object to this proposal until further information is provided to allow an accurate assessment of the collision risk and impact on the national population of this re- introduced protected species. Kinveachy Forest Special Protection Area (SPA) and SAC: This proposal could be progressed with appropriate changes. However, because it could affect internationally important natural heritage interests, we object to this proposal unless it is amended so that the works are done strictly in accordance with the changes detailed in our appraisal below.
Appraisal of the impacts of the proposal and advice
- Landscape and visual impacts
Our advice on this proposal will focus on the potential for significant effects on the Special Landscape Qualities (SLQs) of the Cairngorms National Park (CNP) and is provided in accordance with our Agreement
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2 on roles in advisory casework between NatureScot and Scottish National Park Authorities¹. This should not however be interpreted as meaning there are no other significant effects that need to be considered when determining the application.
Cairngorms National Park The proposed development site lies within the Monadhliath, adjacent to the Cairngorms National Park (CNP) with the closest turbine sited approximately 0.9km from the CNP boundary.
The Monadhliath currently forms an elevated moorland skyline enclosing the western slopes of Strathspey and providing a backdrop from key slopes and summits of the Cairngorms National Park (CNP). The location of the proposed wind farm within the northeast Monadhliath would introduce visibility of turbines to lower lying areas of the Park for the first time. The proposal individually, and cumulatively with the proposed Balnespick Wind Farm, would significantly adversely affect five of the Special Landscape Qualities (SLQs) of the CNP during the day and associated lighting would extend these effects after dark. These impacts would be to a degree that would result in evident and noticeable material changes to the SLQs of the CNP such that the objectives of the designation and overall integrity would be compromised.
Accounting for the site’s elevation and location immediately northwest of the CNP it is considered unlikely that the significant effects identified could be notably reduced through a reduction in turbine height or number. We therefore consider that these effects are unlikely to be overcome through re-design or removal of turbines.
We have considered other interests and taken them into account in reaching our conclusion on this proposal.
This proposal will have significant adverse effects on the special qualities of the Cairngorms National Park such that the objectives of the designation and overall integrity of the area would be compromised. We therefore object to this proposal.
We provide further comments on the effects on the Special Landscape Qualities in Annex 1 to this letter.
Monadhliath Wild Land Area (WLA 20) Although the site boundary overlaps slightly with the Monadhliath Wild Land Area (WLA 20), the nearest turbine would be approximately 0.1km from WLA 20 and no associated infrastructure would be sited within the Wild Land Area.
The proposal would introduce very obvious forms of human influence across a number of summits within WLA 20, detracting from the current awe-inspiring simplicity of the rounded hills. In addition, the turbines would introduce a new landmark feature at close proximity, providing orientation to views within the interior of the WLA, both along the glen floor and higher up the side slopes, substantially reducing the sense of risk. These effects would extend into the night as a result of the turbine lighting and would result in a significant effect on Wild Land Qualities (WLQs) 1 and 2.
We therefore advise that the proposed development would result in a significant effect on Wild Land Qualities (WLQs) 1 and 2 of WLA20. We provide further comments in Annex 2 to this letter.
1 See: https://www.nature.scot/doc/agreement-roles-advisory-casework-between-naturescot-and-scottish-national- park-authorities.
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3
- Protected areas a. European sites
River Spey Special Area of Conservation (SAC) Turbines 1 – 8 are within the catchment of the River Spey SAC which is protected for its Atlantic salmon, sea lamprey, freshwater pearl mussel and otter populations.
The site’s status means that the requirements of the Conservation (Natural Habitats, &c.) Regulations 1994 as amended (the ‘Habitats Regulations’) apply or, for reserved matters, The Conservation of Habitats and Species Regulations 2017. Consequently, the Scottish Government is required to consider the effect of the proposal on the SAC before it can be consented (commonly known as Habitats Regulations Appraisal). Our website has a summary of the legislative requirements².
Our advice is that this proposal is likely to have a significant effect on the interests of this SAC through the risk of sediment release to watercourses, and on otters from the potential for disturbance. Consequently, the Scottish Government, as competent authority, is required to carry out an appropriate assessment in view of the site’s conservation objectives for its qualifying interests.
In relation to the risk of sediment release to watercourses: To help you do this, we propose to carry out an appraisal to inform your appropriate assessment. To enable us to carry out this appraisal, the following information is required:
Assessment of the potential risk of peat and non-peat sediments (regolith) being released into watercourses connected to the SAC. This should include:
• Within the River Spey catchment, further peat depth probing to be undertaken at a higher resolution, covering the requested micrositing limits around the proposed infrastructure. This information should be considered in the Peat and Landslide Hazard Risk Assessment (PLHRA). This is to allow a finer scale assessment of the peat slide risk within the proposed micrositing limits. • Where areas of medium or high peat slide risk are identified within the 100m micrositing limit further assessment and details of appropriate location-specific mitigation will be required, so as to demonstrate how any risk to the SAC will be mitigated. Where infrastructure is located close to the break in slope and use of the micrositing limit could alter the predicted direction it would travel, this should also be considered in the assessment. • Provision of a basic geomorphological assessment of the terrain (with accompanying map) which focuses on potential sediment sources in the vicinity of the proposed construction works, and on slopes that drain into tributaries of the SAC. • Assessment of the risk to watercourses from both acute sediment release through localised slope failure events, and longer-term sediment release through erosion. Particular attention should be given to the proximity of any locally steep-sided glacial deposits to proposed excavations; steeper areas of hill slope to be crossed by new track construction/upgraded track and turbine foundations; and burn bank morphology, composition and stability at any watercourse crossings of tributaries draining into the SAC. • Demonstration of how the findings of this assessment have influenced the layout and design of infrastructure and details of location-specific mitigation measures that will be deployed to minimise the risk of any sediments reaching the SAC.
2 See: https://www.nature.scot/professional-advice/protected-areas-and-species/protected-species/legal- framework/habitats-directive-and-habitats-regulations.
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4 This additional information is required to clarify the peat slide risk, and to ensure that the applicants have assessed the risk from non-peat sediments, in order that these can be effectively mitigated. We requested assessment of these issues at scoping, and that the need for baseline surveys for freshwater pearl mussel, salmon and sea lamprey was considered in accordance with our guidance.
In addition, we note that the PLHRA has only considered the impact of landslide associated with the construction phase of the development and has not considered any risk that may arise from peatland restoration (although outside the footprint there are areas of restored peatland just to the west of turbine 8, and other areas of restoration are proposed between turbines 2 and 3 as part of the proposed Outline Habitat Management and Biodiversity Enhancement Plan (OHMBEP)). Peatland Action guidance on best practice for restoration of peatland and assessment of peatland instability during restoration should be considered, so that any risks arising from this can be mitigated³.
Once this information has been provided, we will be able to give further consideration to this proposal.
In relation to disturbance to otters: We advise that this proposal is also likely to have a significant effect on SAC otters through the potential for disturbance, particularly during the proposed OHMBEP works. We advise that on the basis of the information provided, if the proposal is carried out strictly in accordance with the following mitigation, our conclusion is that the proposal will not adversely affect the integrity of the site:
• A Species Protection Plan for otters is to be agreed with the consenting authority in consultation with NatureScot. This should set out how impacts will be avoided and minimised, following the principles outlined in our standing advice at: https://www.nature.scot/doc/standing-advice- planning-consultations-otters.
This is because the proposed development lies in close proximity to the SAC and the proposed habitat enhancement measures overlap with parts of the SAC. There is potential for disturbance to otters but this could be mitigated through an appropriate Species Protection Plan.
Kinveachy Forest Special Protection Area (SPA) and SAC The proposed development site lies 0.6km from this SPA and SAC, with the nearest turbine around 1km from the boundary. The SPA is protected for breeding capercaillie and Scottish crossbill. The SAC is protected for its Caledonian forest and Bog woodland.
Although baseline conditions indicate that the wind farm itself would be unlikely to affect the features of the SPA and SAC, the proposed expansion of woodland into the wind farm site as part of the Outline Habitat Management and Biodiversity Enhancement Plan could create an increased risk of collision for capercaillie. In addition, although we recognise the potential benefits of woodland expansion, there are also potential risks to the Caledonian forest, particularly where planting is proposed, which have not been considered in the EIAR.
Our advice is that this proposal is likely to have a significant effect on the SPA capercaillie population and the SAC Caledonian Forest. Consequently, the Scottish Government, as competent authority, is required to carry out an appropriate assessment in view of the sites’ conservation objectives for its qualifying interests. To help you do this, we advise that on the basis of the information provided, if the proposal is carried out
3 See: https://www.nature.scot/doc/naturescot-research-report-1259-risk-based-approach-peatland-restoration-and- peat-instability.
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5 strictly in accordance with the following changes, our conclusion is that the proposal will not adversely affect the integrity of the site: i) Turbines 1 and 2 should not be microsited closer to the SAC/SPA boundary (they are currently around 1km from the SPA/SAC boundary). ii) If the wind farm is consented, the final Habitat Management and Biodiversity Enhancement Plan should be agreed with the consenting authority in consultation with NatureScot. The Plan should include the following mitigation: • There should be no tree planting within 1km of the proposed turbines. • Tree regeneration within 1km of the proposed turbines should be managed to ensure it does not increase the collision risk to capercaillie. Details of how this would be achieved should be included in the final Plan. • There should be no additional fencing within the Plan area. • A Species Protection Plan for capercaillie. This should set out the mitigation that would be in place to avoid the risk of disturbance to capercaillie during works associated with the Plan. • Expansion of pine woodland within the combined regeneration and buffer zone around the core Caledonian Pinewood Inventory area should be achieved by natural regeneration.
The appraisal we carried out considered the impact of the proposals on the following factors:
Kinveachy Forest SPA • There is a likely significant effect for the following SPAs, protected for capercaillie, which are within dispersal distance of the proposed development: Darnaway and Lethen Forest SPA (located to the north-east of the proposed development); and Kinveachy Forest, Abernethy Forest, Craigmore Wood, Anagach Woods and Cairngorms SPAs (located to the east and south-east of the proposed development). • The risk of collision and disturbance to capercaillie from the proposed wind farm itself is likely to be low, provided turbines are not microsited closer to the SPA. This is due to the existing baseline, including habitats on site, and distance and location of the proposed wind farm in relation to the above SPAs and capercaillie records. • The proposed woodland expansion within the Outline Habitat Management and Biodiversity Enhancement Plan could however change this existing baseline through increasing habitat suitability within and closer to the proposed wind farm. This could increase the collision risk to capercaillie — although evidence suggests that capercaillie are likely to be displaced by operational turbines, there is also evidence that complete avoidance does not occur with observations from mainland Europe indicating that capercaillie collisions with turbine bases do occur. This risk would need to be mitigated by ensuring there is no increase in tree cover within 1km of the proposed turbines. • Woodland management is proposed close to the SPA and other areas of suitable habitat for capercaillie. A Species Protection Plan would be required to set out the necessary mitigation to avoid the risk of disturbance to lekking and breeding capercaillie. • There should be no additional fencing within the Plan area as fencing close to suitable capercaillie habitat could increase the risk of collision to capercaillie. We recommend instead that any woodland expansion proposals would need secured by an effective Deer Management Plan.
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6 Kinveachy Forest SAC b. • Scottish Forestry guidance is that opportunities for natural regeneration should be maximised in the core Caledonian Pinewood Inventory sites and their combined regeneration and buffer zone. Although expanding the Caledonian forest at this location through natural regeneration would be beneficial and in line with existing management for the SAC, we consider that it would be inappropriate to plant trees at this location due to risk of introducing pathogens such as Dothistroma, and introducing trees of an inappropriate genotype for the site.
Kinveachy Forest Site of Special Scientific Interest (SSSI) The proposed development site includes part of this SSSI, with the nearest turbine around 0.1km from the SSSI boundary. The SSSI is protected for its breeding bird assemblage and native pinewood.
In relation to the breeding bird assemblage feature of the SSSI, there are natural heritage interests of national importance on the site, which could be affected by the proposal. We require further information (detailed below) to determine if the proposal will affect the integrity of the SSSI. We therefore object to the proposal until the further information detailed below is obtained from the applicant and considered by the Energy Consents Unit: • A further year of bird survey work is to be completed across the proposed development site, following the methods set out in our bird survey guidance at: https://www.nature.scot/doc/recommended-bird-survey-methods-inform-impact-assessment- onshore-windfarms.
The breeding bird assemblage is a woodland bird assemblage. The applicants should note that this includes a range of woodland birds such as black grouse, osprey and red kite, and is not limited to capercaillie, Scottish crossbill and crested tit. We recommend that the applicants contact us to agree the scope of additional survey work required. Depending on the outcome of the initial results further survey work may be required. Following this, assessment of impacts will be required, which considers the potential for collision risk, disturbance and displacement. We will comment further once the additional information is available.
Our advice for the native pinewood feature is covered by the advice for the Kinveachy Forest SAC above.
c. The Slochd Geological Conservation Review (GCR) Site Although the proposed wind farm itself will not affect this site, the EIAR has not assessed potential impacts from the Outline Habitat Management and Biodiversity Enhancement Plan which includes proposals for woodland expansion within the GCR site. This could obscure the “rock outcrops” which the GCR site is important for. Should woodland expansion be proposed within the Slochd GCR site we recommend that the final Habitat Management and Biodiversity Enhancement Plan includes the following mitigation: • Should the wind farm be consented, any proposals for woodland expansion within The Slochd GCR site should follow the mitigation and management measures outlined in NatureScot’s Geological Conservation Review Sites – Forestry and Woodland Standing Advice and Guidance.
4 See: https://www.nature.scot/doc/standing-advice-and-guidance-forestry-and-woodland-planning-geological- conservation-review-sites-and.
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7 Sections 2.1.1 and 2.1.2 of the above guidance describes the mitigation and management measures that would be required to ensure that planting and natural regeneration does not affect the nationally important geological features of the site. These refer to the “crucial” and “context” areas of the GCR site. A map of these areas is provided in Annex 3 to this letter.
- Wider Countryside birds Due to shortfalls in the survey and assessment undertaken, we advise that there is insufficient information to assess the impacts of this proposal on Annex 1 birds in the wider countryside, in particular the Natural Heritage Zone (NHZ) 10 and national populations of white-tailed eagles.
• In relation to white-tailed eagle, we therefore object to this proposal until further information is provided to allow an accurate assessment of the collision risk to white-tailed eagles. • In relation to other Annex 1 birds in the wider countryside, we therefore advise that a further year of bird survey work is completed across the proposed development site following our guidance5.
Further advice for white-tailed eagles The calculated annual collision rate for white-tailed eagle from this proposal is very high. It would seem likely that flights recorded are the adults from a nearby territory and their offspring, but the vantage point survey results do not indicate if the flights recorded were adult or juvenile birds. In addition, only one year of survey work has covered the south-eastern part of the site (our guidance recommends 2 years); contextual information from the Highland Raptor Study Group has not been obtained; and the timing of survey work over a limited temporal range means that collision rate could have been underestimated. There is therefore insufficient information to assess the collision risk to white-tailed eagles.
There is evidence from Europe that white-tailed eagle territories with 3km of operating wind farms have lower occupancy and lower productivity than nests beyond this distance. It is unclear whether this is the result of collision mortality to adults, which are then replaced by new birds, resulting in these territories becoming ‘sinks’. We are only aware of one pair of white-tailed eagle within NHZ10. The proposed development could therefore reduce the range of the recovering white-tailed eagle population.
The predicted collision risk would also add significantly to a growing cumulative collision risk at a national level. Taking into account other recent wind farm applications, across Scotland the cumulative annual collision risk for white-tailed eagle is currently more than 14 birds per year. This is likely to result in significant impacts on the growth rate of the national population of this re-introduced protected species, which will slow the rate of range expansion and hinder progress towards restoring its former range across Scotland.
We advise that in the first instance the applicants contact the Highland Raptor Study Group to request desk study information on any white-tailed eagle territories within 6km of the site as well as any available satellite tag data. If satellite tag data is available we recommend that a Kernel Density analysis is undertaken to identify the core areas of use of any territories. Although this will not provide a collision risk estimate it will help to indicate how much the proposed development site is used by white-tailed eagle and the requirement for further survey work. At this stage we advise that one further year of vantage point survey work is likely to be required across the whole of the proposed development site, with an additional
5 See: https://www.nature.scot/doc/recommended-bird-survey-methods-inform-impact-assessment-onshore- windfarms.
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8 year (i.e. two further years in total) covering the south-east part of the site in which turbines 1 to 8 are located.
Further advice on Annex 1 birds in the wider countryside There is currently insufficient information to assess the potential impacts to Annex 1 birds in the wider countryside. This is due to the survey limitations listed in Technical Appendix 8.1 of the EIAR, notably the lack of survey coverage outside the red line application boundary which does not follow our guidance; shortfalls in the timing of breeding bird surveys within the wind farm site itself; because the eight turbines in the south-east section of the proposed development site have only been covered by one year of survey work (contrary to our guidance which recommends two years of survey work); and because the applicants do not appear to have accessed data held by the Highland Raptor Study Group which could have aided their assessment. The timing of vantage point surveys during the 2023 breeding season also provides limited temporal spread and may have underestimated flight activity. Given the scale of the proposal and sensitivity of this site we consider that survey undertaken to date is inadequate to complete an assessment of the impacts to Annex 1 birds in the wider countryside.
For both of these issues, we recommend that the applicants contact us to agree the scope of survey work required. Depending on the outcome of the initial results further survey and assessment may be required. Assessment of impacts will be required to consider the potential for collision risk, disturbance and displacement both from the proposed development on its own (including the proposed OHMBEP) and in combination with other developments (at the NHZ10 scale). Again, we recommend that the applicants contact us to agree the scope of this assessment. We will comment further once the additional information is available.
- Priority peatland habitats We have assessed the quality and sensitivity of the peatland on the site using our framework and template in Annex 1 of our peatland guidance, the information presented in the EIAR and our background knowledge of the location.
We are largely in agreement with the assessment carried out by the applicants, which indicates that most of the site has been modified for sporting or livestock purposes, and indicators of near natural condition are limited. The site does not appear to contain indicators of a high quality habitat within the development area, and we therefore advise that predicted impacts could be offset by adequate peatland restoration.
The EIAR indicates that there will be direct loss of 17.69ha of peatland habitats, and combined direct and with indirect losses of around 116ha. The Outline Habitat Management and Biodiversity Enhancement Plan provided with the application proposes peatland restoration through ground works and peatland enhancement through plug planting, but it lacks detail, the area of restoration proposed is not clear, and some of the methods proposed may not follow best practice. It therefore appears that the restoration proposed is currently not sufficient to offset the impacts to peatland habitats from the development. We would be looking for a plan for this site to follow our guidance6 and for the amount of offsetting proposed to be in the region of 1:10.
6 See: https://www.nature.scot/doc/advising-peatland-carbon-rich-soils-and-priority-peatland-habitats-development- management.
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9
- Protected species We fulfil our advisory role on protected species through the provision of standing advice and do not expect to be consulted other than in exceptional circumstances not covered by the relevant standing advice available on our website. Where a licence from NatureScot will be required by the applicant before they can proceed with the development, you would need to satisfy yourself that the licensing tests set out in those regulations are likely to be met before an application can be approved.
At scoping we advised that the EIAR should demonstrate that all survey, assessment and mitigation has followed our standing advice for protected species. It is not clear from the EIAR whether all survey work has followed our guidance (e.g. water vole surveys do not seem to have been done at the recommended time of year, and survey coverage for otters is unclear). There is also no consideration of mountain hare as a protected species, which we identified as a consideration at scoping. We recommend that all further survey work should follow the standing advice on our website, and should also cover areas proposed for habitat enhancement, see: https://www.nature.scot/professional-advice/planning-and- development/planning-and-development-advice/planning-and-development-protected-species.
Bats Some of the guidance referenced in the bat assessment is now out of date and the proxy weather data source is some distance from the site. Despite these short comings, we agree that under the current baseline conditions bat activity levels would be expected to be low over the site most of the time, but there could be activity spikes during warm summer nights. We would therefore recommend that the applicants implement the following additional mitigation for bats: • Pitching the blades out of the wind (“feathering”) to reduce rotation speeds below 2rpm while idling.
The reduction in speed resulting from feathering compared with normal idling may reduce fatality rates by up to 50%. As this option does not result in any loss of output, as best practice, it is recommended wherever it is practically possible and there remains uncertainty over the risk posed to bats. It can be applied at any site with a blade pitch control system which can be automated using SCADA data. Proposed habitat enhancement measures could also increase the site suitability for bats and management may be required to reduce the collision risk to bats. For further advice see: https://www.nature.scot/doc/bats- and-onshore-wind-turbines-survey-assessment-and-mitigation.
Scottish wildcat Apparently suitable areas of scrub exist in riparian areas within the proposed development site, and there are wildcat records in the wider area. We therefore recommend that, should the proposed development be consented, a camera survey is undertaken around the scrub habitats within 200m of any proposed works, in advance of construction starting. If evidence is found of wildcat using the wider area, we advise that further follow-up camera surveys would be required immediately before work commences because wildcats are very mobile and can move den sites. This is particularly important if the works are to be done between April to August inclusive (the female denning season). If a wildcat is recorded it should be assumed that it is denning or resting within the scrub unless further survey work is undertaken to establish the frequency and timing of activity as evidence the location is not used for resting. The applicants should
7 See: https://www.nature.scot/professional-advice/planning-and-development/planning-and-development- advice/planning-and-development-protected-species. 8 The applicants should follow our guidance for identification at: https://www.nature.scot/doc/definition-wildcat- updated-guidance.
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10 also note that if applying for a licence, mitigation should include carrying out works outside the female denning season (i.e. work should avoid April to August inclusive). For further advice see: https://www.nature.scot/doc/standing-advice-planning-consultations-wildcats. If wildcat habitat could be affected by the proposed development we would also recommend compensation measures.
Mountain hare Should this proposal be consented a Species Protection Plan will be required for mountain hares. This should include details of the measures proposed to minimise impacts on mountain hares; a summary of any residual impacts once these measures are taken into account; and details of any licensing requirements, including the proposed method for detecting and protecting any young hares ahead of groundworks commencing. This should follow our standing advice at: https://www.nature.scot/doc/standing-advice- planning-consultations-mountain-hare.
The Outline Habitat Management and Biodiversity Enhancement Plan suggests mountain hare control for woodland management. As mountain hare are a protected species a licence would be required from NatureScot if this is proposed. We advise that control should not be considered unless monitoring shows that hares are having a measurable effect on natural regeneration.
Please let Karen Reid ([email protected]) know if you or the applicants require any further information or advice from us in relation to this proposal.
The advice in this letter is provided by NatureScot, the operating name of Scottish Natural Heritage.
Yours sincerely
Chris Donald Head of Operations, Central Highland
Cc Roddy Dowell, Highland Council; Emma Bryce, Cairngorms National Park Authority
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11 Annex 1 — Cairngorms National Park
Assessment Baseline
The proposed development would be situated just outside the north-western boundary of the Cairngorms National Park, to the west of the A9 and south of Strathdearn, across an area of elevated moorland that forms part of the north-eastern Monadhliath mountains.
The Monadhliath comprise a long range of rolling moorland hills and plateaux with summits of 550 to 850m AOD. The landscape is homogenous and almost featureless, with no distinct summits or patterns. Much of the area lies within the Monadhliath Wild Land Area (WLA 20) for which the description reads: ‘The hills appear stunning in their simplicity, openness and immense scale, offering from their tops elevated views across a succession of sweeping landform horizons that often seem to continue infinitely in every direction’. The Cairngorms National Park boundary follows the eastern ridge of the hills. Described as forming a ‘visual backdrop and a more secluded hinterland to the landscape character areas within Strathspey, the backdrop seems ‘to merge into an undulating skyline without any clearly identifiable features’10, appearing ‘remote and formidable11’ from the closer, settled lower ground.
The Landscape Character Type (LCT) description for host LCT 221 – Rolling Uplands – Inverness identifies: ‘a strong sense of openness and exposure’ from hilltops and plateaux and an uninhabited interior with ‘a strong perception of remoteness’ forming an extensive area of rolling hills ‘extending far beyond the district boundary and into the Cairngorms National Park’ where the LCT merges across the boundary into LCT 125 Rolling Uplands — Cairngorms. The open nature of this landscape affords a high level of intervisibility across the hills, WLA 20 and Cairngorms National Park, which are of a high sensitivity to wind development.
LCT 221 accommodates a number of existing wind farms. Operational and consented wind farms¹2 broadly form five clusters, the majority of which are located in visually discreet lower-lying basins. Dunmaglass Wind Farm is an exception due to the location of turbines on more elevated ground resulting in increased prominence from the Monadhliath WLA. The closest operational wind farms to the proposal are Farr and Glen Kyllachy although, from the edge of the Park, Farr, Glen Kyllachy and Dumnaglass have a limited influence appearing as relatively distant and compact features in the wider landscape. This is illustrated from Viewpoint (VP) 8 – Carn Sleamhuinn13, VP 10 – Track near Geal Charn Mor¹4, and VP 16 — Carn an Fhreicaedain Summit15. At 5.8km, Tom nan Clach is the closest operational wind farm to the Park boundary, however, like Moy, it appears as a relatively compact feature in the wider landscape due to its height (125m to blade tip)