Item5Appendix2HRA20210227DETLaraigView
Cairngorms
Item 5 Appendix 2 8 December 2023 National Park Authority Üghdarras Pàirc Nàiseanta a’ Mhonaidh Ruaidh
Agenda item 5
Appendix 2
2021/0227/DET
Habitats regulations appraisal
HABITATS REGULATIONS APPRAISAL
Planning reference and proposal information | 2021/0227/DETErection of 7 houses, restaurant (including a micro-gin distillery) and production building, Lairig View, Aviemore, PH22 IQD |
Appraised by | Karen Aldridge, Planning Ecological Advice Officer |
Date | 29 November 2023 |
Checked by | NatureScot |
Date | XXXX |
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INFORMATION
European site details |
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Name of European site(s) potentially affected |
1. Kinveachy Forest SPA’ |
2. River Spey SAC |
Qualifying interest(s) |
1. Kinveachy Forest SPABreeding — capercaillie and Scottish crossbill |
2. River Spey SACAtlantic salmon, fresh water pearl mussel, sea lamprey and otter |
Conservation objectives for qualifying interests |
1. Kinveachy Forest SPA:To avoid deterioration of the habitats of the qualifying species or significant disturbance to thequalifying species, thus ensuring that the integrity of the site is maintained; andTo ensure for the qualifying species that the following are maintained in the long term:Population of the species as a viable component of the siteDistribution of the species within siteDistribution and extent of habitats supporting the speciesStructure, function and supporting processes of habitats supporting the speciesNo significant disturbance of the species |
2. River Spey SAC:Conservation Objective 2. To ensure that the integrity of the River Spey SAC is restored bymeeting objectives 2a, 2b, 2c for each qualifying feature (and 2d for freshwater pearl mussel): |
It is recognised that effects on capercaillie at any one of the Badenoch and Strathspey capercaillie SPAs or associated woodlands shown on the map in Annex I has the potential to affect the wider capercaillie metapopulation of Badenoch and Strathspey. Attention has been focused in this HRA on the woods likely to be used regularly for recreation by users of the proposed development site, which in this case are Kinvechie Forest SPA and the associated Boat of Garten, Loch Garten, Glenmore and Rothiemurchus woods (woods I, J, K, L, M, N and O on the map). Other capercaillie SPAs and woods were considered during the initial phase of the assessment (see Annex I question 3) but detectable effects were ruled out, so they have not been included in this HRA. If however the HRA had concluded an adverse effect on site integrity, or required mitigation, then all of the capercaillie SPAs in Badenoch and Strathspey would have been reassessed in relation to potential effects on the metapopulation.
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2b. Restore the distribution of freshwater pearl mussel throughout the site
2c. Restore the habitats supporting freshwater pearl mussel within the site and availability of food
2d. Restore the distribution and viability of freshwater pearl mussel host species and their supporting habitats
2a. Restore the population of freshwater pearl mussel as a viable component of the site
2b. Maintain the distribution of sea lamprey throughout the site
2c. Maintain the habitats supporting sea lamprey within the site and availability of food
2a. Maintain the population of sea lamprey as a viable component of the site
2b. Restore the distribution of Atlantic salmon throughout the site
2c. Restore the habitats supporting Atlantic salmon within the site and availability of food
2a. Restore the population of Atlantic salmon, including range of genetic types, as a viable component of the site
2b. Maintain the distribution of otter throughout the site
2c. Maintain the habitats supporting otter within the site and availability of food
2a. Maintain the population of otter as a viable component of the site
Conservation Objective I. To ensure that the qualifying features of the River Spey SAC are in favourable condition and make an appropriate contribution to achieving favourable conservation status
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APPRAISAL
STAGE 1: |
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What is the plan or project? |
Relevant summary details of proposal (including location, timing, methods, etc) |
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The proposal is for the erection of 7 houses and a restaurant building (including a micro-gindistillery within the restaurant buildings), production/storage building and parking, plus associatedinfrastructure. Connection to mains water and sewerage is proposed. The proposal involves builtdevelopment across the majority of the site with a small proportion of space for landscape planting.The garden ground for the northern dwellings will include the 6m riparian buffer zone (the bufferrecommended by SEPA for riparian buffers).The site comprises land with two dwellings (a stone-built house and a wooden chalet) andassociated outbuildings, now with prior approval for demolition. The ground around the buildingsincludes mature trees, a watercourse that connects to the River Spey SAC to the east, roughgrassland and wetland habitat. |
STAGE 2: |
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Is the plan or project directly connected with or necessary for the management of theEuropean site for nature conservation? |
No. |
STAGE 3: |
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Is the plan or project (either alone or in-combination with other plans or projects)likely to have a significant effect on the site(s)? |
1. Kinveachy Forest SPA |
Capercaillie — there is a risk of LSE from the potential long-term disturbance through increasedhuman activity by the addition of the occupants of the proposed development – as explainedwithin Annex 1. |
Scottish crossbill none of their habitat will be affected therefore there will be no LSE. Scottishcrossbill are therefore not considered further in this assessment. |
2. River Spey SAC |
There is potential for LSE on all qualifying interests due to change in water quality, due potentialfor pollution during construction activity from sediment run off, particularly during the re-profilingworks in close proximity to the watercourse.In addition, disturbance to otter could occur during construction and occupation through humanactivity. |
STAGE 4: |
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Undertake an Appropriate Assessment of the implications for the site(s) in view ofthe(ir) conservation objectives |
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1. Kinveachy Forest SPA |
Distribution of the species within the site: |
The distribution of capercaillie within the site will not be affected as additional use of woods(described in Annex I) is not likely to result in additional off path activity, therefore thisconservation objective will be met. |
Distribution and extent of habitats supporting the species; Structure, function andsupporting processes of habitats supporting the species: |
There will be no effect on the structure, function or supporting processes of the habitatssupporting capercaillie as a result of the proposed development, therefore this conservationobjective will be met. |
No significant disturbance of the species |
See Annexes I‑III for detailed assessment. In summary, there would not be additional disturbanceto capercaillie over and above what is already occurring through use of existing routes in woods I,J, K, L, M, N and O. Therefore this conservation objective can be met. |
Population of the species as a viable component of the site: |
As the other conservation objectives can be met, the population of capercaillie should not beaffected and so this conservation objective will be met. |
In conclusion, all conservation objectives can be met. |
2. River Spey SAC |
FWPM, Atlantic Salmon & Sea Lamprey |
2b. Restore/Maintain the distribution throughout the site |
No works are proposed within the River Spey SAC, so there will be no direct impacts upon thedistribution of these species within the designated site. Indirect impacts may arise fromconstruction activities leading to pollution events e.g. sediments or chemicals reaching the SACimpacting upon the current distribution of FWPM, salmon or lamprey.A CMS (submitted July 2022) details methods for managing silt produced during constructionoperations and also details storage of oil and fuel. Providing the CMS is adhered to during theentirety of construction, the risk of pollution events should be minimised. It should be noted thatno works should take place within the 6m buffer to the watercourse, which should include thestorage of materials. All construction activities should adhere to standard good practicedocuments (GPP5, GPP8, GPP21 & GPP22 as a minimum). |
2c. Restore/Maintain the habitats supporting freshwater pearl mussel within the siteand availability of food |
The current and potential distribution of habitats supporting Atlantic salmon. lamprey and FWPM within the |
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SAC would not be directly affected as no development will occur within the SAC.
However, pollution from construction activities upstream, could potentially affect supporting habitats if significant amounts of sediment reach the SAC and cause smothering, reducing the distribution and extent of habitat suitable for spawning and juvenile salmon and habitats suitable for supporting FWPM/lamprey (long term).
However, mitigation measures identified for 2b above would reduce the risk of pollution reaching the watercourse to a minimal level and so this conservation objective would be met.
2d. Restore the distribution and viability of freshwater pearl mussel host species and their supporting habitats
The distribution and viability of FWPM host species (Atlantic salmon & sea trout) would not be directly affected as there are no works in stream therefore no barriers being created by the potential development (although the burn is likely to offer little suitable habitat for FWPM).
As discussed in 2b & 2c, there is potential for pollution from construction activities to indirectly affect the habitats supporting these species which may in turn lead to a change in distribution or in change in health of the supporting species. However, with the implementation of the mitigation mentioned in 2b the risk of pollution events therefore the development would not hinder the distribution or vitality of the host species.
2a. Restore/Maintain the population of Atlantic salmon (including range of genetic types), Freshwater Pearl Mussel and Sea Lamprey, as a viable component of the site
As the other conservation objectives can be met with mitigation, the proposed development would not hinder or prevent the restoration or maintained of the qualifying species as a viable component of the site. Therefore, this conservation objective would be met.
Otter
A survey was carried out for a 100m buffer of the proposed development site, which does not meet the requirements of NatureScot guidance (https://www.nature.scot/species-planning-advice- otters) which states that 200m up and downstream should be surveyed. However, based on the habitat, size of watercourse, proximity to existing residential housing along with the A9 and the Aviemore orbital footpath (which is well used by people including for dog walking), professional judgement is that the habitat is suboptimal for breeding, although it may be used by foraging otter. Therefore, further survey work for otter covering the small area between the surveyed area and the A9 to the west is not required on this occasion.
2b. Maintain the distribution of otter throughout the site
The survey did not identify any signs of otter using the Milton Burn, however it is likely to support otter from the River Spey SAC, with good terrestrial habitats surrounding the burn for supporting otter prey species (e.g. amphibians). Given the proximity of the burn to the A9 and residential properties, it is considered likely that otter using the burn are habituated to some levels of noise and disturbance.
The CMS (submitted July 2022) details an otter protection plan, which would limit disturbance to otter therefore the current distribution of otter within the SAC, should not be negatively impacted upon, meeting
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this conservation objective.
2c. Maintain the habitats supporting otter within the site and availability of food
The distribution of habitats supporting otter would not be directly affected. The pollution issues identified for the other freshwater species mentioned, could affect otter prey species, however the mitigation measures would reduce the risk of this occurring to a minimal level and so the conservation objective would be met.
2a. Maintain the population of otter as a viable component of the site
As the other conservation objectives can be met for otter with the mitigation included in the proposal, the proposed development would not hinder or prevent the maintenance of the population of otter as a viable component of site, therefore this conservation objective would be met.
Conservation Objective I. To ensure that the qualifying features of the River Spey SAC are in favourable condition and make an appropriate contribution to achieving favourable conservation status
As all the other conservation objectives would be met, the proposed development would not prevent or hinder the condition or conservation status of the qualifying interests of the SAC, and so this conservation objective would be met.
STAGE 5: |
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Can it be ascertained that there will not be an adverse effect on site integrity? |
1. Kinveachy Forest SPA |
Yes, as all conservation objectives are met it is possible to conclude that there will not be anadverse effect on site integrity. |
2. River Spey SAC |
Yes, providing the following are conditioned, it is possible to conclude that there will not be anadverse effect on site integrity: •The CMS (submitted July 2022) should be implemented in full — which includes the provisionon an Ecological/Environmental Clerk of Works to oversee all elements of construction. •The Otter Protection Plan (within CMS) should be implemented in full — which includes apreconstruction survey for otter, to cover all suitable habitats within 200m and restrictionson construction times. |
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Annex I 2021/0227/DET: Erection of 7 houses, restaurant (including a micro-gin distillery) and production building, Lairig View, Grampian Road, Aviemore, PH22 IQD
QI. Is the proposed development likely to change levels of human activity or patterns of recreation around the proposed development/associated settlement?QI: This and Q2 are included as screening questions to filter out any developments that aren’t likely to have changed levels or patterns of recreation. | Yes, there would be an increase in the level of human activity (but not patterns of recreation).Using the 2.07 occupancy rate applied for the LDP (in the absence of a robust alternative), theproposed development of 7 dwellings could result in an additional 15 people staying at theproposed development.The existing population of Aviemore was estimated to be around 3,800 people in 2020 (based onNational Records of Scotland 2019 mid-year estimate of the population).In the planning system, there is consent for additional residential units, as listed in Annex II. Usingthe 2.07 occupancy rate applied for the LDP (in the absence of a robust alternative), this wouldamount to an additional 609 people, giving a potential population of around 4,410.Adding an additional 15 people to the existing Aviemore population would increase the currentpopulation* by around 0.4%. This would be a moderate increase in the potential number of peopleusing existing paths and routes, should all the residents use them (which not all residents will).This is not a significant increase.*based on occupancy of existing properties, not including consented but not yet builtThe potential population of Aviemore (ie baseline existing population plus consented but not yetbuilt) would increase the baseline existing population by around 16% to 4,410 people. Adding 15people from the proposed development to this would result in an increase in the potentialpopulation of a further 0.3%. Again, this is not a significant increase.Consideration needs to be given as to whether the addition of the proposed development on topof the potential population is likely to result in changes in the levels or patterns of human activityand recreation. |
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There are a number of existing promoted and well used paths and routes in Aviemore and the surrounding area, as seen in the figure below (taken from the Aviemore Paths leaflet https://www.visitaviemore.com/wp-content/uploads/2013/09/CNPA.Paper_.1911.Aviemore- Paths.pdf). There are also informal un-promoted but well used routes that connect with formal paths and roads. Residents of the proposed development (marked by the black star in the below figure) are likely to use the promoted paths, due to information being available about them.
There is no reason to believe that people staying at the proposed development would undertake a different pattern of recreation to existing users of paths and routes in Aviemore and the surrounding area.
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Q2. Are capercaillie woods significantly more accessible from this development site than from other parts of the associated settlement?Q2: This is included to ensure the effect of otherwisesmall-scale development sites particularly close to capercaillie woods are adequately considered. Evidencefrom settlements in Strathspey where houses areadjacent to woodlands indicates that networks ofinformal paths and trails have developed within thewoods linking back gardens with formal path networksand other popular local destinations (eg primaryschools). Such paths are likely to be used by visitors. | No. The closest entry point to a known capercaillie wood (Kinveachy Forest, wood I on theBadenoch and Strathspey capercaillie woodlands map in Annex III, part of the KinveachyForest SPA for capercaillie and Scottish crossbill) is approximately Ikm from the proposeddevelopment along either public roads/footpaths or the Aviemore Orbital route and then publicroads/footpaths through Milton of Burnside (some of which are relatively steep). As this is areasonable distance from the proposed development, and makes use of existing routes, theproposed development site is not considered to be more accessible than from other parts ofAviemore. |
If QI & Q2 = No, conclusion is no significant disturbance to capercaillie and assessment ends here | |
If QI or Q2 = Yes, continue to Q3 | |
Q3. Which capercaillie woods are likely to be used regularly for recreation by users of the development site at detectable levels? (list all)Q3: This is included to identify which capercaillie woodsare likely to be used for recreation by users of non-housing development sites at levels that would bedetectable. The answer will be assessed usingprofessional judgement based on knowledge of existingpatterns of recreation around settlements and in thelocal area, the relative appeal of the capercaillie woodsconcerned compared to other recreational opportunitiesin the area, the volume of recreational visits likely to begenerated by the development site, and informed bynational survey data (eg on the distances people travelfor recreational visits). | None at detectable levels.The closest entry point to a known capercaillie wood (Kinveachy Forest, wood I on the map inAnnex III and part of the Kinveachy Forest SPA) is approximately Ikm from the proposeddevelopment, up a relatively steep route located at Milton of Burnside as described in question 2.The tracks and paths in Kinveachy are well used by residents of Burnside for recreation includingdog walking, as well as by other residents of Aviemore and other people from the wider area.Due to the distance between the proposed development and the entry point to Kinveachy, it isunlikely that a significant proportion of visitors staying at the proposed development wouldrecreate in Kinveachy on a regular basis, as they are more likely to use other flatter, closer andpromoted routes such as the Aviemore orbital, and/or visit other promoted visitor locations inthe area surrounding Aviemore, such as Glenmore, Loch Garten and Rothiemurchus.In recent years Kinveachy has become known for downhill biking, with illicit route creation causingdisturbance in sensitive capercaillie areas. However, the proportion of people staying at theproposed development who might visit Kinveachy and who would be equipped, inclined andcapable of doing the downhill biking routes that are causing existing disturbance issues in thewood would be very small.It is reasonable to expect people staying at the proposed development to also visit other areas |
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Q4. Are residents / users of this development site predicted to undertake any off path recreational activities in any of the woods identified at Q3 at detectable levels?Q4: This is included because any off path recreationaluse in capercaillie woods will result in significantdisturbance and require mitigation.If Q4 = No for any woods, continue to Q5 | No. There is no reason to believe that people staying in the proposed development would notfollow existing patterns of behaviour and use existing paths and tracks for recreation and dogwalking. |
If Q4 = Yes for any woods, mitigation is needed. Note and continue to Q5. | |
Q5: Are each of the woods identified at Q3 already established locations for recreation?Q5: This is included because if users of thedevelopment site are likely to access previouslyinfrequently-visited capercaillie woods, or parts of thesewoods, for recreation, significant disturbance is likelyand mitigation is needed. This will be answered on thebasis of professional knowledge. | Yes. See answers to questions 1, 2 and 3. |
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If Q5 = No for any woods, mitigation is needed. Note and continue to Q6. | |
If Q5 = Yes for any woods, continue to Q6 | |
Q6: For each of the woods identified at Q3, are users of the development site predicted to have different temporal patterns of recreational use to any existing visitors, or to undertake a different profile of activities?(eg. more dog walking, or early morning use)Q6: This is included because some types of recreationare particularly disturbing to capercaillie; and increasedlevels of these types of recreation will cause significantdisturbance and require mitigation. This will beanswered on the basis of professional knowledge onexisting patterns of recreational use and whether eachlocation is sufficiently close and/or convenient in relationto the development site and patterns of travel fromthere, to be used by users of the development fordifferent recreational activities or at different times ofday. For example, capercaillie woods with safe routesfor dogs that are located close to development sites arelikely to be used for early morning &/or after work dogwalking. | No. The woods are all already well used at a variety times of day for walking, running and cycling,as well as dog walking, by both residents and visitors to Aviemore and the wider area. Peoplestaying at the proposed development are unlikely to undertake a different temporal pattern orprofile of activities compared to existing use. |
If Q6 = yes for any woods, mitigation is needed. Note and continue to Q7 | |
If Q6 = No for any woods, continue to Q7 | |
Q7: For each of the woods identified at Q3, could the predicted level of use by residents / users of the development site significantly increase overall levels of recreational use?Q7: This is included because a significant increase inrecreational use could result in significant disturbance tocapercaillie, even in situations where the capercaillie | No. There would not be a detectable or significant increase in human activity in KinveachyForest or the capercaillie woodlands associated with Boat of Garten, Loch Garten, and Glenmoreand Rothiemurchus (woods I, J, K, L, M, N and O in Annex III). |
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wood is already popular for recreation, and no changesto current recreational patterns / activities or off pathactivities are predicted. The answer was assessed onthe basis of professional judgement of current levels ofuse and whether the increase is likely to be more thanapproximately 10%. | |
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If Q4‑7 = No for all woods, conclusion is no significant disturbance to capercaillie and assessment ends here | |
If Q4, 5, 6 and/or 7 = Yes for any woods, mitigation is needed | |
Conclusion: Is mitigation needed as a consequence of this development site in relation to each wood listed at Q3? | None required. |
Reasons mitigation needed: | n/a |
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Annex II – information on planning applications with consent but not yet built The number of people per application site has, unless otherwise stated, been calculated using the 2.07 person occupancy figure used for the LDP assessment as explained in the answer to question I of this document:
GRAMPIAN ROAD NEAR ACHANTOUL 3 people based on number of guest beds per the approved floor plan: 20/03708/FUL Conversion of garage annex to form guest bedroom accommodation, Carn Mhor Guest House, The Sheiling, Aviemore, PH22 IQD
INVERDRUIE 13 people: 2016/0158/DET Erection of 6 dwellings, upgrade current access point and a new access track formed; private drainage (shared treatment plant and soakaway), Land 175M SE Of Heatherbank, Rothiemurchus, Aviemore
SOUTH END OUTSIDE AVIEMORE 2 people: 20/04360/FUL Demolition of garage and replacement with double garage with granny flat, Kinmundy, Grampian Road, Aviemore, PH22 IRH
SOUTH END OF AVIEMORE LA TAVERNA 8 people based on 4 double beds in each unit as per the approved floor plan: 19/00846/FUL Construction of 4no. units for holiday letting, High Range Motel, 19 Grampian Road, Aviemore, PH22 IPT
NEXT TO HAPPY HAGGIS 56 people: 2019/0363/DET, Erection of three blocks of flats (27 units) with associated parking and access, Development Site On Former Filling Station Grampian Road Aviemore Highland
NEAR HOSPITAL 34 people: 2019/0298/DET, Spey House Phase 2 — Development of 14 no dwellings including 6no terraced houses, 4no bungalows and 4no cottage flats, Land 20M South East of Spey House, Cairngorm Technology Park, Dalfaber Drive, Aviemore
Part of HI in LDP: 193 people: Applications associated with 2018/0184/MSC Satisfy the Conditions of Planning Permission PPA-270‑2126 for residential units, Land North West Of Dalfaber Farm, Dalfaber Drive, Aviemore
PART OF H2 in LDP: 79 people: 2016/0224/DET Proposed 30 flats and 8 terraced units, Land 30M West Of 31 Allt Mor, Aviemore
PART OF AHR MI in LDP: 33 units of the 140 already built, so for the remaining units it will be 221 people: 05/306/CP Erection of 140 dwellings, construction of roads and services and landscaping, Horse Field (Land North Of Scandinavian Village), Aviemore
SEAFIELD PLACE –22/04334/FUL- Conversion of a garage into a one bedroom self contained flat. 2 people.
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Annex III – Badenoch and Strathspey capercaillie woods map
A North Grantown B Castle Grant & Mid Port C Tom an Aird Anagach Woods D E [ Anagach Woods SPA ] Slochd F North Carr-Bridge G Drochan & Drumuillie H Craigmore Woods [ Craigmore Woods SPA] Kinveachy Forest Cam 575 [ Kinveachy Forest SPA ] J Loch Vaa K Garten Woods [ Abernethy Forest SPA] L Forest Lodge M North Rothiemurchus [Cairngorms SPA ] chan MV Camelache N South Rothiemurchus UNTAINS Doune O Glenmore The Folchar सिया Ga-share Bone Dreggie Mnox Glenbeg Grondale 471 D Bure Actinaliamet GRANTOWN- 190 ON-SPEY Craggan Dasale A936 Bridge bridge Congash Duthit A939 HELS OF CROMDALE Sinchel F Skyn Lynemera 722 A9 of Caut Deeyan Lochanhully Chase Invorlaidr E Carrbridge 10 A95 Broatia H S Gaome Bridge of Nethy Bridge Dir Brown Drumul Na Cullachie Gliemere 14 Brchtele Dainahaitnach Lattach Lodge 566 Bern Groslaan Boat of Enddich wachy Cave lt Largy J Barten Forest Avialachan Aundorach Tore Hi P Tulloch Forest Lodge Auchigourish Dorback Sure Braas of Danboth Milhos 501 Tomintoul 04 Delmahe Carn Madhorach Abermethy BRE Clashnor Chapaltown College of Scalan Gan M Dat A939 792 Blaimamanow The Secach 718 Aviemore Farauh Dafaber استار M ridge Forsel Rachelite Can There ar Qu 700 200 711 Cod Edesta Омекслан Аса Www Advin Chorec Upper Derraid Auchnajallin Leftoch A95 Glaschoil Parascry Geag ath Cotta Camerdry ABC Mains of Dalvery Drumin 430 Glenlivet Shinvil Auchbrick Cam 547 Tomnavoulin Dallery Dám Gare Anchnarta Speyside Wa Almack Scre P Inshriach Car Oenan Q Uath Lochans area A Srte 511 Nothiemeno Canne Faraninge Саторите Speybank Cate 919 A Chailteach Kingraig Tincula 10 Ho P More 000 A9 NO 21 Fushiebridge GLEN ON CAIRN GORM The Bruach Forest of Glenavon CAIRNGORMS NATIONAL PARK Gen 17 Ralne 1068 1246 Geow Cham 073 Cock Bridga Coln Castle Delsalamph Cergarft Toma 704 800 Can Lea Se ud
- Bom Cov Eleg Inshriach Lynhat Leag Forest BT Gelen Gon CAIRNGORM Gara 1215 Shdt KINGUSSIE 1500 Gerh Insh Sokat C 100 Saintange 1100 1100K Newlatumace Bracriach 1184 1100 Sien Markie Drumquish Gler Banchor 1205 43007 Oog Chomarang MOUNTAINS 1006 BEN MACDUI Onge Laggan Balgown A86 Crethie Lodge Lynk crack Ledge Tromie Anell 627 Gen Feshie Aman 1049 Gen Gro 1291 Geke INETY Cairn Toul 210 907 016 100 1007 BEINN A BHUURD Cubt Mana Suchf 1002 Lebaidh an Darm Chache 1124 BEN AVON 117 Cam D 900 000 Cong 5 Calv Lebe Dullay The Devila Mnadh است Mwo Kilometers Mal Balnait Maini of Capercaillie woodland in Badenoch and Strathspey. Reproduced by permission of Ordnance Survey on behalf of HMSO. © Crown copyright and database right 2018. All rights reserved. Ordnance Survey Licence number 100040965 Cairngorms National Park Authority Nature Scot page 15 of 15