Harryburn Wind Farm. Technical Appendix Peat Management Plan Innogy Renewables UK Ltd

Transcription

1 Harryburn Wind Farm Technical Appendix 11.2 Peat Management Plan Innogy Renewables UK Ltd SLR Ref: Version No: Final April 2017

2 Harryburn Wind farm CONTENTS 1.0 NON TECHNICAL SUMMARY INTRODUCTION METHODOLOGY Guidance POTENTIAL IMPACTS ON PEAT FROM CONSTRUCTION SITE ACTIVITIES Wind Turbines Crane Hardstanding Construction Compounds Borrow Pits Access Tracks Cable Trenching PROPOSED MITIGATION DURING CONSTRUCTION Wind Turbine Foundations Crane Hardstanding s and Temporary Compounds Access Tracks Floating Access Tracks Excavated Access Tracks Peat Excavation, Storage and Transport Restoration SITE BASED PEAT EXCAVATION AND REUSE ASSESSMENT PEAT EXCAVATION CONSIDERATIONS CONCLUSION CLOSURE TABLES Table 6-1: Excavation Materials Management Plan Table 7-2: Excavated Materials Assessment of Suitability Figure 1 Figure 2 Site Locality FIGURES Drift Geology (showing extent of peat) APPENDIX Appendix A Excavated Materials Spreadsheet

3 Harryburn Wind farm NON TECHNICAL SUMMARY SLR Consulting Ltd (SLR) was commissioned by Innogy Renewables UK Limited (Innogy) to undertake a Peat Management Plan (PMP) for inclusion as a Technical Appendix to the Environmental Impact Assessment (EIA) for the development of the proposed Harryburn Wind Farm (the proposed development ). The proposed development would be located approximately 2.5km east of the village of Leadhills, in the administrative boundary of South Lanarkshire Council. The proposed development (as described in Chapter 3 Description of the Development, of the ES) would consist of wind turbine generators (referred to as turbines ) and associated infrastructure. This Stage 1 Peat Management Plan (PMP) has been prepared by SLR Consulting Ltd and its purpose is to ensure that there has been systematic consideration of peat and peaty soils management and a quantitative assessment throughout the development process. This Peat Management Plan (PMP) has been prepared by SLR Consulting Ltd and its purpose is to ensure that there has been systematic consideration of peat management and a quantitative assessment throughout the construction process. This plan includes all materials to be excavated as part of the construction process, including peaty soils and peat. Detailed peat depth probing and peat characterisation has been undertaken across the site (as outlined in Technical Appendix 11.1 of the ES (Peat Landslide Hazard and Risk Assessment)). This was used to inform the design of the development in order to avoid areas of deeper peat or areas of peat instability. Using site specific peat depth probing data, the potential volume of peat and soils that might be excavated as a consequence of constructing the development has been estimated. Excavated peat associated with development on peat is not classed as a waste provided it is suitable (from an engineering as well as environmental perspective) for a required and predetermined use as part of construction works and reinstatement on site 1, (SR, SEPA, January 2012). It has been shown using best practice guidelines that as a result of the site design, the volume of peat and soils that would be excavated is low and can be readily reused on site as part of the site construction and restoration. As a result, no surplus peat would be generated. This document provides initial volume estimates for peat excavation and reuse and outlines recommendations for the handling and storage of peat during construction and restoration of the site, in line with current best practice guidelines. 1 Guidance on the Assessment of Peat Volumes, Reuse of Excavated Peat and the Minimisation of Waste (Scottish Renewables, SEPA, January 2012).

4 Harryburn Wind farm INTRODUCTION This Peat Management Plan (PMP) considers the excavation of peat and soil across the site as a result of construction of the proposed development. It considers the potential for minimising excavation and disturbance in order to reduce any unnecessary surplus of peaty soils and peat. The best management option to minimise potential surplus peat is to prevent its excavation. Therefore, the original design of the development has aimed to minimise peat excavation where possible. Discussion of design considerations to avoid deeper areas of peat is included in Chapter 13: Hydrology and Hydrogeology and Chapter 11: Geology, Technical Appendix 11.1: Peat Landslide Hazard and Risk Assessment and Chapter 2: Project Design of the ES. SEPA has provided a waste hierarchy of management approaches through which the effectiveness of the approach to peat management is optimised at development sites as summarised below (SEPA , SEPA ): prevention: avoiding generating excess peat during construction (e.g. by avoiding peat areas or by using construction methods that do not require excavation such as floating tracks); re-use: use peat produced on site in restoration of hardstandings or landscaping, provided that its use is fully justified and suitable; recycling/recovery/treatment: modify peat produced on site for use as fuel, or as a compost/soil conditioner, or dewater peat to improve its mechanical properties in support of re-use; storage: temporarily store peat on-site (for example, during short periods in the construction phase) and then re-use. The guidance identifies three main stages in the development process and describes what data should be gathered and assessed at each to inform a sitespecific PMP: Stage 1: Environmental Impact Assessment (EIA); Stage 2: Post-consent / pre-construction; and Stage 3: Construction. This PMP has been prepared in accordance with the principles in the guidance for Stage 1 and 2 and proposes that prevention and re-use are the most appropriate means of managing peat excavated during construction at this site, Stage 3. This report details the methodologies required to assess all potential surplus materials and presents preliminary estimates of the expected volume of excavated materials and required reuse volumes for reinstatement and restoration purposes. In particular, this report considers the construction of access tracks, site compound, turbine foundations and all other associated infrastructure which result in the excavation of peat and sub-soils potentially resulting in surplus materials. 2 SEPA Regulatory Position Statement Developments on Peat (SEPA, February 2010). 3 Guidance on the Assessment of Peat Volumes, Reuse of Excavated Peat and the Minimisation of Waste (SR, SEPA, January 2012).

5 Harryburn Wind farm Many of the issues typically associated with peat on a wind farm site have been accommodated by modifying the development layout to avoid potentially difficult or sensitive areas. Areas that have been avoided include: areas of deep peat, requiring potentially large volumes of excavation; areas of moderate to steep slopes (where site infrastructure might increase the chance of peat instability); and areas of sensitive ecological and hydrological habitat. This report estimates the extent of materials which would be generated during the construction phase and identifies potential areas where peat could be reused through the following: the avoidance of creating surplus materials, and the reuse of materials on site. The assessment is based on the description of the proposed development provided in Chapter 3: Project Description of the ES.

6 Harryburn Wind farm METHODOLOGY To determine the extent of excavated material across the site as a result of the development, the following have been considered: the amount of excavated materials arising from construction activities on site; and the extent of excavated materials derived from any excavations, which if not stored correctly (on a temporary basis), or used appropriately in restoration, is at risk of releasing CO 2 emissions. This PMP assesses the volumes of excavated material sourced from the site, to calculate site specific volumes based on factors including: excavations around turbines what materials would be re-used and how; length of access tracks would peat be removed and where it would be used in landscaping/reinstatement in an appropriate fashion; other infrastructure - can materials from site be used during reinstatement works. An assessment of the peat balance has been undertaken to determine the materials available on site for use in reinstatement. 3.1 Guidance There are a number of guidance documents appropriate to the activities planned on site which have been used to guide this assessment. These have included a number of documents including Scottish Guidance documents which demonstrate best practice, as follows: Guidance on the assessment of peat volumes, reuse of excavated peat and the minimisation of waste (SR, SEPA, January 2012); Guidance on Developments on Peatland - Site Surveys Guidance on conducting site surveys on peatland. (SNH 2014); SEPA Regulatory Position Statement Developments on Peat (SEPA, February 2010); Good practice during wind farm construction (SR, SNH, SEPA, FCS; October 2010); Floating roads on peat (SNH, FCS; August 2010); Peat Landslide Hazard and Risk Assessments: Best Practice Guide for Proposed Electricity Generation Developments Scottish Government Constructed tracks in the Scottish Uplands (SNH, March 2005); Calculating carbon savings from wind farms on Scottish peat lands, a new approach (Nayak et al., 2008, 2011); and The Waste Management Licensing (Scotland) Regulations 2011.

7 Harryburn Wind farm POTENTIAL IMPACTS ON PEAT FROM CONSTRUCTION SITE ACTIVITIES The following section outlines the impacts anticipated relating to peat at the proposed development site, summarising the key issues for the main wind farm infrastructure anticipated at the Harryburn Site. 4.1 Wind Turbines Wind turbine foundations in peatlands normally require full and permanent excavation of peat to competent strata, with temporary excavation of peat from a wider diameter to enable safe access to the base of the excavation. The resulting peat generated could be considered as a permanent loss, unless satisfactory re-use could be achieved within the development site. The peat would be used to reinstate track shoulders, around crane hardstandings and turbine bases. 4.2 Crane Hardstanding In order to assemble the wind turbine and enable servicing during operation, crane pads are constructed adjacent to each wind turbine. These must be sufficient to take the weight of both the crane and turbine components, and therefore excavation to underlying competent strata is required. Without adequate drainage controls, permanent excavation may disrupt natural hydrological pathways, appropriate drainage control will be implemented as part of the construction process. Crane pads remain in place for the life of the wind farm to enable routine inspection and maintenance. Peat generated from these excavations would be considered a permanent loss, unless satisfactory re-use could be achieved within the development site. 4.3 Construction Compounds A temporary compound would be provided during the construction phase to enable storage of construction materials, turbine components and fuel, siting of welfare facilities and site offices. Because of their temporary nature, peat excavated for compounds would normally be stored and reinstated, and therefore re-use is required. 4.4 Borrow Pits No borrow pits to be required on site. 4.5 Access Tracks Access tracks are required to enable passage of construction and servicing traffic around the wind farm site. Over peatlands, the choice of access track design reflects the peat depths along the route, with shallow peat / organic soils <1m deep excavated to competent strata (cut and fill tracks), and deeper peats overlain by floating tracks (with no excavation). There is only one short section of road to T7 with deeper peat along track which would be constructed as floating road.

8 Harryburn Wind farm Access tracks are permanent infrastructure, peat excavated for cut and fill would be considered a permanent loss, unless the peat can be re-used elsewhere on site, such as along track verges. No excavations are undertaken for floating tracks, and therefore there is no associated peat excavation. In excavated tracks, the surface vegetation (i.e. habitat) would be lost unless stored and reinstated elsewhere, we would re-use excavated turves, soil and peat on verges and shoulders of track shoulders and hardstandings for landscaping and restoration purposes. Access tracks have the potential to disrupt natural hydrological drainage pathways, appropriate drainage would be designed to mitigate this and this would be detailed in the Construction Environmental Management Plan (CEMP) and Surface Water Management Plan (SWMP). 4.6 Cable Trenching Electrical cabling would be buried or ducted adjacent to the access track network (cable trenching), either into existing peat (requires excavation, laying and backfilling) or wherever possible ducts are laid within reinstated material at the sides of floated tracks (no excavation of in-situ peat required). Where excavation is required, peat generated from cable trenching is normally replaced at its point of origin, and therefore is not considered a volume loss and re-use is a certainty.

9 Harryburn Wind farm PROPOSED MITIGATION DURING CONSTRUCTION There are a number of ways in which detailed design and construction activities can be specified to minimise impacts on peatlands. The detailed construction environmental mitigation is outlined in the draft CEMP; the following section outlines briefly the likely mitigation based on the reuse of peat specific to key elements of the wind farm development (Figure 1). 5.1 Wind Turbine Foundations Wind turbine foundations represent permanent excavation and the primary mitigation measure is to locate the wind turbines to avoid the areas of deepest peat, thereby reducing excavated volumes. Based on peat probing, the turbine locations for the proposed development are located on peaty soils/peat with an average peat depth of 0.36m, ranging from 0.08m to 1.0m. Technically the majority of the material underlying proposed turbines and crane hardstanding is not classified as peat (<0.5m) with only four turbines are located in peat in excess of 0.5m deep Of these turbines T3, T1, T6 and T7, located on peat >0.5m and have been subject of minor micrositing, to avoid deeper peat. The remaining the turbines are located on relatively thin peaty soils and thin peat which would be reused around the turbines and crane hardstanding areas. 5.2 Crane Hardstanding s and Temporary Compounds In relation to crane hardstanding, guidance is to avoid their full reinstatement postconstruction, given the likelihood of re-use for maintenance activities associated with the wind turbines. In relation to temporary compounds, the following good practice guidance 4 applies: peat stripped from compound and hard standing areas would require particularly careful storage due to its volume, and the relatively long residence times for stored peat; Stripped turves are generally used for final restoration, however where turves are insufficient or vegetation regeneration requires reseeding and temporary fencing may be considered around compound areas undergoing restoration in order to prevent grazing. The peat would be used around the edge of the crane hardstanding and turbine bases, it would not cover crane pad as this is an engineered fill and would not be suitable for peat reinstatement; and the choice of seed mix if required for reseeding should be appropriate to the ecological and hydrological conditions of the restored compound location and surrounding habitats. 5.3 Access Tracks In comparison to infrastructure specific to wind turbines, there is considerably more guidance available to support access track design in peatlands. Guidance 5 is 4 Environmental Good Practice on Site C650, CIRIA, 2005;

10 Harryburn Wind farm generally focused on floating tracks and excavated tracks, and is summarised in the following text. 5.4 Floating Access Tracks Over deeper peat (typically >1.0m), floating tracks are used to remove the requirement for peat excavation and limit disruption of hydrological pathways. The success of construction requires careful planning to take account of the unique characteristics of peat soils. Specific guidance 6 is available on design, the duration and timing of construction, the sequence of construction and the re-use of peat on the shoulders of the floating access track Design of Floating Access Tracks The following issues would be considered during detailed design of floating access tracks: adopting conservative values for peat geotechnical properties during detailed design (post-consent); applying a maximum depth rule whereby an individual layer of geogrid and aggregate should not normally exceed 450mm without another layer of geogrid being added; on gently sloping ground and where the access track runs transverse to the prevailing slope, accommodating natural hydrological pathways such as flushes and peat pipes through installation of a permanent conduit within or underneath the track and allowing for as much diffuse discharge (while minimising disturbance to existing peatland) on the downslope as possible; ensuring transitions between floating tracks and excavated tracks (or other forms of track not subject to long term settlement) are staged in order to minimise likelihood of track failure at the boundary between construction types; scheduling access track construction to accommodate for, and reduce, peat settlement characteristics; and Re-use of existing roads (with upgrading if required), where possible Duration and Timing of Construction of Floating Access Tracks The critical factor in successful construction of floating access tracks is the timescale of construction, and the following good practice guidance is provided: the settlement characteristics of peat; should be accommodated by appropriate scheduling of access track construction, as follows: 5 Good Practice during Windfarm Construction, Version 3, a joint publication by Scottish Renewables, Scottish Natural Heritage, Scottish Environment Protection Agency, Forestry Commission Scotland and Historic Environment Scotland, Floating roads on peat (SNH, FCS; August 2010).

11 Harryburn Wind farm prior to construction works, the setting out the centreline of the proposed access track to identify any ground instability concerns or particularly wet zones; identifying stop rules, i.e. weather dependent criteria for cessation of access track construction based on local meteorological data; maximising the interval between material deliveries over newly constructed access tracks that are still observed to be within the primary consolidation phase; Sequence of Construction The sequence of construction of floating tracks is normally stipulated in guidance provided by the supplier of the geotextile or geogrid layer, and suppliers are often involved in the detailed access track design. Good practice in relation to the sequence of access track construction is as follows: retaining rather than stripping the vegetation layer (i.e. the acrotelm, providing tensile strength), and laying the first geotextile/geogrid directly on the peat surface; adding the first rock layer; adding the second geotextile/geogrid, and add overlying graded rockfill as a running surface; heavy plant and Heavy Goods Vehicles (HGV) using the access tracks during the construction period should be trafficked slowly in the centre of the track to minimise dynamic loading from cornering, breaking and accelerating; ensuring wheel loads should remain at least 0.5m from the edge of the geogrid; and toolbox talks and subsequent feedback to construction and maintenance workers and drivers to emphasise the importance of the implementing the above measures Use of Peat as Trackside Shoulders A key opportunity to re-use peat is to employ it in landscaping of constructed access tracks. Wedge-shaped reinstatement at the margins of a floating access track (which is elevated above the peat surface) is referred to as shoulders, and good practice guidance is as follows: re-using peat excavated as shoulders adjacent to the floating track; peat shoulders should taper from just below the track sides (thereby preventing over high shoulders from causing ponding on the track surface) to join the surrounding peat surface, keeping as natural a profile as possible to tie in with existing slope profiles; and limiting the width of peat shoulders to avoid unnecessary smothering of intact vegetation adjacent to the floating track.

12 Harryburn Wind farm Excavated Access Tracks Excavated tracks require complete excavation of peat to a competent substrate. Excavated tracks are generally undertaken where peat depths are less than 1m. This peat would require storage ahead of re-use elsewhere on site. Good practice guidance relates mainly to drainage in association with excavated tracks: trackside ditches should capture surface water (within the acrotelm) before it reaches the road; interceptor drains should be shallow and flat bottomed (and preferably entirely within the acrotelm to limit drawdown of the water table); any stripped peat turves should be placed back in the invert and sides of the ditch to assist regeneration; and culverts and cross drains would be installed under excavated tracks to maintain subsurface drainage pathways (such as natural soil pipes or flushes). Discharge from constructed drainage should allow for as much diffuse dispersion of clean (silt free) water as possible while minimising disturbance to existing peatland as far as possible. Silt mitigation measures would be incorporated into all constructed drainage as per the requirements of the draft CEMP. Although excavation is normally undertaken in peat of < 1.0m, there is a possibility of minor slippage from the cut face of the peat mass. Accordingly: free faces should be inspected for evidence of instability (cracking, bulging, excessive discharge of water or sudden cessation in discharge); and where significant depths of peat are to be stored adjacent to an excavation, stability analysis should be conducted to determine Factor of Safety (FoS) and an acceptable FoS adopted for loaded areas. Cable Trenches Cable trenches either require peat excavation specifically for this purpose alongside excavated tracks, or they can be constructed within landscaping of shoulders adjacent to floating tracks. Guidance is as follows: utilise peat shoulders for cable lays where possible to minimise peat excavations specifically for this purpose, in this case, peat shoulders should be 1.0m to 1.5m thick; where cable trenching is constructed adjacent to a floating road, ensure the trench is backfilled to prevent void filling by material migration; minimise time between excavation of the cable trench and peat reinstatement, preferably avoiding excavation until the electrical contractor has cables on-site ready for installation; and avoid incorporating substrate materials in the excavation, to minimise contamination of the peat to be reinstated. Replace excavated materials sequentially.

13 Harryburn Wind farm An alternative technique which is being considered for some areas is cable ploughing this would also minimise disturbance and a requirement to re-use peat. These techniques would also apply to open areas away from the infrastructure, however it would be anticipated that most of the cables will be at ot close to the proposed layout. 5.6 Peat Excavation, Storage and Transport As peat is to be re-used or reinstated on the site with the intention that its supported habitat continues to be viable, the following good practice apply: Excavation Excavated peat should be excavated as turves, including the acrotelm (surface vegetation) and a layer of adjoining catotelm (more humified peat) typically up to 500mm thick in total, or as blocks of catotelm; the acrotelm should not be separated from its underlying peat (see Figure 5.1). the turves should be as large as possible to minimise desiccation during storage; contamination of excavated peat with substrate materials should be avoided; and consider timing of excavation activities to avoid very wet weather and multiple handling to minimise the likelihood of excavated peat losing structural integrity. If possible, intact full depth acrotelm layers from the top surface of the peat deposit should be extracted. This technique will maintain connectivity between the surface vegetation and the partially decomposed upper layers of the catotelm. Figure 5.1 Schematic Section of peat acrotelmic/catotelmic relationship Storage Any peat generated as part of the construction process should be stored appropriately and follow the key principles listed as follows: peat turves should be stored in a wet condition or irrigated in order to prevent desiccation (once dried, peat will not rewet);

14 Harryburn Wind farm stockpiling of peat should be in large volumes to minimise exposure to wind and sun (and desiccation), but with due consideration for slope stability; excavated peat and topsoils should be stored to a maximum of 1m thickness; stores of non-turf (catotelm) peat should be bladed off to reduce the surface area and desiccation of the stored peat; and monitor areas of steep peat and peat storage areas during periods of very wet weather, or during snowmelt, to identify early signs of peat instability Temporary Storage Initial excavation volumes for construction of turbine and crane hardstanding foundations would range between 150m 3 and 2000m 3. Based on the volume of peaty soils/peat encountered at site, volumes ranging from as little as ~100m 3 to ~600m 3 of peat would require excavation from the turbine bases. As an example, for the average volume (~300m 3 ), this would require a temporary storage area near to the construction works of approximately 20m x 15m to a height of 1.0m. Where peat cannot be transferred immediately to an appropriate restoration area, short term storage would be required. In this case, the following good practice applies: peat should be stored around the turbine perimeter at sufficient distance from the cut face to prevent overburden induced failure, local gullies, diffuse drainage lines (or very wet ground) and locally steep slopes should be avoided for peat storage; stored upper turves (incorporating vegetation) should be organised and identified according to NVC community (assisted by the Environmental Clerk of Works, ECoW) for reinstatement adjacent to like communities in the intact surrounding peat blanket; drying of stored peat should be avoided by irrigation (although this is unlikely to be significant for peat materials stored less than 2 months). For crane pads, borrow pits and compounds (with longer term storage requirements), the following good practice applies: peat generated from crane pad locations should be transported directly to its allocated restoration location, to minimise the volume being stockpiled with the possibility of drying out; stores of catotelmic peat should be bladed off to reduce their surface area and minimise desiccation; where transport cannot be undertaken immediately, stored peat should be irrigated to limit drying and stored on a geotextile mat to promote stability; monitoring of large areas of peat storage during wet weather or snowmelt should be undertaken to identify any early signs of peat instability Transport Good construction management is essential to ensure timeous movement of peat and soils on site. As such:

15 Harryburn Wind farm movement of turves should be kept to a minimum once excavated, and therefore it is preferable to transport peat planned for translocation and reinstatement to its destination at the time of excavation; and if HGVs that are used for transporting non-peat material are also to be used for peat materials, measures should be taken to minimise cross-contamination of peat soils with other materials Handling A detailed storage and handling plan for peat and soils would form part of the detailed CEMP. These parameters have been determined in light of recent detailed ground investigation with the micro-siting areas for each element of infrastructure. 5.7 Restoration carefully evaluate potential restoration sites, such as borrow pits for their suitability, and agree that these sites are appropriate with the ECoW, landowners and relevant consultees; undertake restoration and revegetation work as soon as possible; where required, consider exclusion of livestock from areas of the site undergoing restoration, to minimise impacts on revegetation; and as far as reasonably practicable, restoration should be carried out concurrently with construction rather than at its conclusion.

16 Harryburn Wind farm SITE BASED PEAT EXCAVATION AND REUSE ASSESSMENT The PMP has been undertaken to support the appliciation for the proposed development, to ensure there is an understanding of the extent of peat on the site, the total amount of peat that might be excavated, and that the re-use of the excavated materials is certain and minimised where possible. The development layout comprises 17 No. wind turbines and associated crane hardstandings, a single access point for construction traffic to the east of the site, onsite access tracks of cut construction, with a small section of floating road, one temporary construction compound and one permanent operations building, cabling and one permanent meteorological mast Peat Probing Background A series of peat probing exercises were undertaken in 2016 by experienced geotechnical and hydrogeological engineers, which fed into the iterative design process of the development. The Phase 1 Peat Probing Site Survey was undertaken in March/April 2016 by experienced geotechnical engineers, following the reconnaissance visit in March During this visit a total of 1021 probes were undertaken across the likely development portion of the site on an approximate 100 m x 100m grid (in line with Scottish Environmental Protection Agency (SEPA) Guidance), a further 482 probes were undertaken as part of the Phase 2 Peat Probing Site Survey (August 2016). The main survey areas of the Phase 1 Peat Survey were located primarily around Harryburn Brae, Peat Hill and Dun Moss where the proposed turbines and infrastructure are located. The areas subject to probing extend over the developable section of the site, extending to the site boundary, or to the limits of soil cover. A combination of exposed shallow bedrock, steep slopes defined the extent of the site survey at this stage. The 100 m x 100 m grid undertaken allowed the site design iterations to be modified and accommodated within the surveyed areas. The Phase 2 Peat Probing Survey visit in August 2016 was undertaken to further assess the potential extent of peat, to address potential areas of concern and to determine extent of peat at proposed infrastructure locations, with particular reference to establishing the extent of superficial cover at turbines and associated infrastructure including compounds, substation and along tracks 7. During this visit a total of 482 probes were undertaken across the site at approximately 50m spacing along the proposed access routes and around all the infrastructure, turbines and crane hardstanding on an approximate 50 m x 50 m grid (in line with SEPA Guidance). The initial reconnaissance visit identified areas or localised pockets of peat which warranted further attention or avoidance and were further investigated as part of the 7 Appendix 9.1: Peat Slide Hazard Risk Assessment, Figures 5 and 6.

17 Harryburn Wind farm Phase 1 survey. The majority of the site was found to have a thin (<0.5 m) peaty soil cover over glacial till. The overall conclusion regarding peat stability is that there is a negligible to low risk of peat instability over most of the site. The conclusions are detailed in Technical Appendix 11.1, Peat Landslide Hazard and Risk Assessment. The site is generally covered in peaty soils and peat, therefore deeper peat areas (generally greater than 1m (and in most instances >0.5m)) have been avoided where possible. No evidence of significant peat instability was noted on the site, primarily as it is generally on flat lying to gentle slopes, with thin fibrous peaty soil. A number of locally deep areas of peat have been identified and where possible avoided by infrastructure. The layout has been carefully designed to minimise excavating or disturbing localised areas of peat, where possible, and where this cannot be avoided, mitigated by design to limit peat excavation, including avoiding haggy areas of peat and floating roads in areas of deep peat Excavated Peat Volume Estimates Based on the development details, a total volume of excavated peat, sub-soil and topsoil has been calculated (see Table 6.1). It also includes an estimate of the extent of acrotelmic peat (fibrous) vs catotelmic peat (amorphous) which would be excavated. Reuse estimates are discussed in Section 7 (Table 7.1). The figures used in the following table, are derived from the excavated materials worksheet included as Appendix A.

18 Soil and Peat Management Plan Harryburn Wind farm April 2017 Table 6-1: Excavation Materials Management Plan Method Volume of Excavated material m 3 How much of this can be reused on site % Opportunity for Avoidance or minimisation of Excavated material Re-use Requirements Hierarchy Adherence Limitations and Constraints Excavated Access Tracks Total length of the access tracks would be 16km and would consist of the following: 12.9km of new access tracks (excavated) of which 3270m is along peat or peaty soils 2.8km of existing access tracks (widened and upgraded); 300m of floating road to T8 Of the total 16km, ~15.7km would be excavated access tracks and these would be located on peaty soil (<0.38m) and thin peat between 0.35 and 0.6m. Average peat thickness along excavated access track is 0.38m. The access track would be a minimum of 5 wide, with 0.5m verges. This volume includes ~78% of soils and peaty soils, which are very 8341 m 3 New Track (3270m x 0.38m x 5m) 6213 m 3 Upgrade Existing Track (2800m x 0.38m x 5m) 2128 m 3 100% The access track route has been subject to a number of design iterations to avoid peat and steep slopes. Where possible track width would be minimised. The peat along the proposed excavated access tracks on the site is very fibrous and does not exhibit thick catotelmic peat. Visually the peat is coarse fibrous peat which is fairly dry and reasonably well drained. There are some areas of thick peat on the route of the site access tracks to T8; this would utilise floated access tracks to minimise disturbance of the peat. Verge Restoration and visual screening, particularly along access track. Sections of the route may require cut and fill and these slopes would require restoration to minimise visual impact ~18210m 3 of excavated peat and peaty soil would be used along access tracks. Further restoration materials may be required to restore cut and fill sections of the track. Avoidance was first level of screening to avoid areas of thicker peat. Routing has been planned on thinner peat or peaty soils where possible. The layout design has been guided by constraints which highlight ecological, hydrogeological and geomorphological all of which identify the peat areas to avoid. As the southern and eastern portion of the site is almost entirely underlain by peat, access track route selection has also been guided by extensive peat probing to establish areas of shallow peat. Detailed assessment may identify further lengths of floating access tracks, which would further reduce requirement for excavation.

19 Soil and Peat Management Plan Harryburn Wind farm April 2017 Method Volume of Excavated material m 3 How much of this can be reused on site % Opportunity for Avoidance or minimisation of Excavated material Re-use Requirements Hierarchy Adherence Limitations and Constraints fibrous and technically a soil rather than peat. The material would all be excavated and as such should be considered as part of overall restoration. All of this fibrous material can be reused and has an inherent strength. Floating Access Tracks It is anticipated that limited floating tracks would be required. This is only a limited stretch of track to T8 0 Not applicable No excavated material except where cable trenches are proposed (see below). Looked at different cut off depths for floating access track. Based on > 1m depth. Verge restoration must avoid impacting existing unexcavated peat. Borrow Pits 0 Turbine Foundations 17 No. turbines With average excavation of 28m diameter x 0.36m (average peat thickness at turbines) ~3766m 3 100% Turbine locations have been subject to a number of design iterations to avoid thicker peat and steep slopes. Average thickness of peat at turbine sites is~0.36m At turbine foundations topsoil would be stripped keeping top 200mm of turf intact. This would be stored adjacent to the base working area and would be limited to 1m height. To reinstate following construction the hardstanding area around the turbine an area of ~ 115 m 3 would be required per turbine, hence a total of 3910m 3 could be Avoided areas of thick peat for turbine bases, identified sites on bedrock or close to bedrock to minimise removal of excessive materials. Detailed ground investigation was undertaken at each turbine, and this did not significantly change the overall assumptions.

20 Soil and Peat Management Plan Harryburn Wind farm April 2017 Method Volume of Excavated material m 3 How much of this can be reused on site % Opportunity for Avoidance or minimisation of Excavated material Re-use Requirements Hierarchy Adherence Limitations and Constraints reused. Crane Pads 17 No. crane hard standings With average excavation of 65m x 40m x 0.36m with additional small areas for cranes and blades (3m x 12m) 7105 m 3 100% Crane hardstanding locations have been influenced by the turbine design iterations to avoid thicker peat and steep slopes. Average thickness of peat at turbine sites is~0.36m; hence crane hard standings would be similar. At crane hardstandings topsoil would be stripped keeping top 200mm of turf intact. This would be stored adjacent to the base working area and would be limited to 1m height. To restore the hardstanding area around the perimeter of the crane hardstanding an area of ~230 m 3 would be required per turbine, hence a total of 3910m 3 could be reused. See issues for turbine bases. Orientation of crane hardstandings to be designed following recent detailed site investigation (SI), to avoid constraints and minimise requirement for peat excavation. Detailed ground investigation was undertaken at each turbine, and this did not significantly change the overall assumptions. Cable Routes Total distance of cabling ~16.0km 16,000m of cables would be located on Peaty Soils and peat over Glacial Till. Using an average for roads at 0.38m peat depth, however in reality, trench depth is unlikely to exceed 1.0m. Total Road Length 6070m x 0.38m x 1.0m 2307m 3 100% Minimised disturbance to drainage by taking cable route along existing access track and around the turbines adjacent to new access tracks. Much of the cable routes are over shallow peaty soils and Glacial Till where complete re-use of the materials on site is envisaged. In areas where the cable route is on rock, the site may require excavation of rock or laying cable in upfilled sections to minimise Suitable excavated materials would be reused to backfill trenches 2307 m 3 Re-use and backfill excavated materials. A site investigation was undertaken which did not change the assumptions.

21 Soil and Peat Management Plan Harryburn Wind farm April 2017 Method Volume of Excavated material m 3 How much of this can be reused on site % Opportunity for Avoidance or minimisation of Excavated material Re-use Requirements Hierarchy Adherence Limitations and Constraints excavation of rock. Temporary Construction Compound 1 No. 50m x 80m the majority of the compound would be located on Glacial Till with a thin average peat thickness of 0.1.m. 50m x 80m x 0.68m 2720 m 3 100% The construction compounds would largely be located on Glacial Till alongside the existing access track. Materials would be reused on site to restore working areas and for appropriate landscaping m 3 Avoided siting temporary compounds on thick peat areas where possible. None Met Mast 1 30m x 30m x 0.4m (x2) 360 m 3 100% The met mast would largely be located on Glacial Till alongside the existing access track. Materials would be reused on site to restore working areas and for appropriate landscaping. 360 m 3 Avoided siting met mast on thick peat areas where possible None Electrical compound 1 No 50m x 80m 50m x 80m x 0.1m 400 m 3 100% The construction compounds would largely be located on Glacial Till alongside the existing access track. Materials would be reused on site to restore working areas and for appropriate landscaping. 750 m 3 Avoided siting temporary compounds on thick peat areas where possible. None Electrical Substation 1 No 80m x 50m 80m x 50m x 0.1m 400 m 3 100% The substation compounds would largely be located on Glacial Till alongside the existing access track. Materials would be reused on site to restore working areas and for appropriate landscaping. 400 m 3 Total Excavated ~24,999 m 3 100% ~31882 m 3 Avoided siting temporary compounds on thick peat areas where possible. None Based on the values indicated there is a balance of materials with no surplus peat anticipated to be generated on site.

22 Harryburn Wind farm PEAT EXCAVATION CONSIDERATIONS This section of the PMP includes the method for dealing with peat which could potentially be classified as waste (only if the above volumes estimate significant quantities of catotelmic peat, which cannot be re-used). Table 7.1: Excavated Materials Reuse Estimate, outlines where the materials likely to be generated on site fall within the Waste Licensing Regulations. It has been concluded that all of the materials to be excavated on site would fall within the non-waste classification as much of the top soil and peaty soils would be re-used on site. The peat ranges from fibrous peat to amorphous peat and is classified based on the von Post classification as ranging from an H 3 to H 9 peat ranging from very slightly decomposed to strongly decomposed. By modification of the track, and micrositing turbines the majority of the peaty soils/peat encountered is fibrous to pseudo fibrous peat (H 3 to H 6 peat) and the thicker amorphous peat has been avoided Technical Appendix - Peat Landslide Hazard and Risk Assessment 9.1

23 Harryburn Wind farm Table 7-2: Excavated Materials Assessment of Suitability Excavated Material Indicative Volume on Site by % of total excavated soils 9 Is there a suitable use for Material 10 Is the Material required for Use on Site Material Classified as a Waste Mineral Soil 10 Yes Yes Not classified as a waste Turf (Surface layer of vegetation and fibrous matt) Acrotelmic Peat and catotelmic peat with H 3 to H 5 classification (very slightly decomposed to slightly decomposed semifibrous with low moisture content) Likely to have suitable structural integrity for reuse on site (fibrous material retains integral structure and can stand unsupported when stockpiled >1m) Catotelmic Peat with H 6 to H 9 classification (very decomposed to strongly decomposed amorphous peat with high moisture content) (amorphous material unable to stand unsupported when stockpiled >1m) 55 Yes Yes Not classified as a waste 30 Yes Yes 5 Not classified as a waste 5 Very limited around site development due to avoidance by design Potentially Potentially Such uses for this type of material are limited, although there may be justification for use to maintain water logged conditions and prevent desiccation of restored area and in some habitat management works such as, gully or ditch blocking where saturated peat is required to mimic mire type habitats and encourage Potentially if not required as part of justifiable restoration or habitat management works Re-use Potential Yes Yes Yes No? Re-use on site Would be reused in reinstatement of access track verges, cut and fill verges, road verges, side slopes and check drains. Peripheral embankments of turbine bases, crane hardstandings and restoration of borrow pits Would be reused in reinstatement of access track verges, cut and fill verges, road verges, side slopes and check drains. Peripheral embankments of turbine bases, crane hardstandings and restoration of borrow pits Method statements to identify how peat is excavated, stored and used would be detailed and agreed through the detailed CEMP. If peat does not require treatment prior to re-use it can be used on site providing adequate justification and method statements are provided and approved by SE. If it is unsuitable for use without treatment then it may be regarded as a waste. However every attempt to avoid this type of peat has been incorporated into the design. 9 Based on a total excavated volume for the site of 24,999 m Is there a suitable use for the material without need for treatment and without risk to the environment or human health

24 Harryburn Wind farm Excavated Material Indicative Volume on Site by % of total excavated soils 9 Is there a suitable use for Material 10 Is the Material required for Use on Site establishment of sphagnum. Material Classified as a Waste Re-use Potential Re-use on site

25 Harryburn Wind farm CONCLUSION The figures shown in the tables suggest that the volumes of peat excavated on site would be re-used without creating surplus materials which would require to be classified as waste. The PMP would be included as part of the CEMP which would been updated with information obtained from the detailed ground investigations prior to construction commencing. The majority of the excavated peat is therefore entirely re-useable as it is predominantly fibrous to pseudo fibrous and easily re-used on site.

26 Harryburn Wind farm CLOSURE This report has been prepared by SLR Consulting Limited with all reasonable skill, care and diligence, and taking account of the manpower and resources devoted to it by agreement with the client. Information reported herein is based on the interpretation of data collected and has been accepted in good faith as being accurate and valid. The writer; Colin Duncan (BSc (Hons), MSc FGS) is a Geologist with over 30 years experience in geological consulting for the minerals, mining, planning, and energy sectors. This report is for the exclusive use of Innogy Renewables UK Ltd; no warranties or guarantees are expressed or should be inferred by any third parties. This report may not be relied upon by other parties without written consent from SLR. SLR disclaims any responsibility to the client and others in respect of any matters outside the agreed scope of the work.

27 Harryburn Wind farm FIGURES Figure 1 Figure 2 Site Locality Drift Geology (showing extent of peat)

28 LEGEND SITE BOUNDARY T14 T13 T12 T11 T15 T10 T9 T8 T16 T17 T7 T6 T4 T5 T3 T2 T1 PROPOSED TURBINE LOCATIONS PROPOSED PERMANENT MET MAST LOCATION PROPOSED ACCESS PROPOSED CRANE HARDSTANDING PROPOSED SUBSTATION COMPOUND PROPOSED CONSTRUCTION COMPOUND 4/5 LOCHSIDE VIEW EDINBURGH PARK EDINBURGH EH12 9DH Site Locality Crown copyright [and database rights] (2017) Expires 06/04/ Kilometres Scale 1:30,000 HARRYBURN WIND FARM Date T: +44 (0) TECHNICAL APPENDIX 11.2 SITE LOCALITY FIGURE 1 APRIL 2017 This drawing and its content are the copyright of SLR Consulting Ltd and may not be reproduced or amended except by prior written permission. SLR Consulting Ltd accepts no liability for any amendments made by other persons.

29 NOTES 1. SUPERFICIAL GEOLOGY DATA OBTAINED VIA BGS WMS. BRITISH GEOLOGICAL SURVEY NERC. ALL RIGHTS RESERVED. LEGEND SITE BOUNDARY PROPOSED TURBINE LOCATIONS T14 T13 T12 T15 T9 T11 T10 T16 T8 T17 T7 T6 T4 T5 T3 T2 T1 PROPOSED PERMANENT MET MAST LOCATION PROPOSED ACCESS TRACK PROPOSED CRANE HARDSTANDING SUPERFICIAL GEOLOGY PROPOSED SUBSTATION COMPOUND PROPOSED CONSTRUCTION COMPOUND ALLUVIUM PEAT RIVER TERRACE DEPOSITS HUMMOCKY GLACIAL DEPOSITS TILL BEDROCK AT OR NEAR SURFACE Superficial Geology Crown copyright [and database rights] (2017) Expires 06/04/ Kilometres Scale 1:40,000 HARRYBURN WIND FARM Date 4/5 LOCHSIDE VIEW EDINBURGH PARK EDINBURGH EH12 9DH T: +44 (0) TECHNICAL APPENDIX 11.2 SUPERFICIAL GEOLOGY FIGURE 2 APRIL 2017 This drawing and its content are the copyright of SLR Consulting Ltd and may not be reproduced or amended except by prior written permission. SLR Consulting Ltd accepts no liability for any amendments made by other persons.

30 Harryburn Wind farm Appendix A Excavated Materials Worksheet

31 Excavated Materials Soils and Peat Harryburn Wind Farm Harryburn Wind Farm - Excavated Materials Worksheet Excavated Reused Length Width Average Depth No Total Volume Excavated m 3 Length Width Average depth No Total Volume Reused m 3 Average peat depth along roads is 0.38m Excavated Tracks (New) Assume 3m wide shoulder. road height 1.0m Excavated Tracks (New on peat or peaty soil) Assume 3m wide shoulder. road height 1.0m Excavated Tracks (Existing to be upgraded (T11 to T17)) Assumes widening existing roads to allow for construction Floating Tracks Assume 3m wide shoulder, road height 1.0m Turbine Foundations Crane Pads Crane pads -blades Cable Routes Based on square base. Average peat depth at turbines 0.36m Assumes 2m 3 per linear metre around base Average peat depth at turbines 0.36m Assumes 2m3 per linear metre around base Fully reinstated Average peat depth along roads is 0.38m Temp Construction Compound Full reinstatement Operations Building Use for landscaping bunds and screening Met mast Use for landscaping bunds and screening TOTAL EXCAVATED VOLUME TOTAL REUSED VOLUME NET BALANCE ACTUAL PEAT EXCAVATED Based on 22.3% peat present

32

33 ABERDEEN 214 Union Street, Aberdeen AB10 1TL, UK T: +44 (0) AYLESBURY 7 Wornal Park, Menmarsh Road, Worminghall, Aylesbury, Buckinghamshire HP18 9PH, UK T: +44 (0) BELFAST Suite 1 Potters Quay, 5 Ravenhill Road, Belfast BT6 8DN, UK, Northern Ireland T: +44 (0) BRADFORD-ON-AVON Treenwood House, Rowden Lane, Bradford-on-Avon, Wiltshire BA15 2AU, UK T: +44 (0) BRISTOL Langford Lodge, 109 Pembroke Road, Clifton, Bristol BS8 3EU, UK T: +44 (0) CAMBRIDGE 8 Stow Court, Stow-cum-Quy, Cambridge CB25 9AS, UK T: + 44 (0) CARDIFF Fulmar House, Beignon Close, Ocean Way, Cardiff CF24 5PB, UK T: +44 (0) CHELMSFORD Unit 77, Waterhouse Business Centre, 2 Cromar Way, Chelmsford, Essex CM1 2QE, UK T: +44 (0) DUBLIN 7 Dundrum Business Park, Windy Arbour, Dundrum, Dublin 14 Ireland T: (0) EDINBURGH 4/5 Lochside View, Edinburgh Park, Edinburgh EH12 9DH, UK T: +44 (0) EXETER 69 Polsloe Road, Exeter EX1 2NF, UK T: + 44 (0) GLASGOW 4 Woodside Place, Charing Cross, Glasgow G3 7QF, UK T: +44 (0) GRENOBLE BuroClub, 157/155 Cours Berriat, Grenoble Cedex 1, France T: +33 (0) GUILDFORD 65 Woodbridge Road, Guildford Surrey GU1 4RD, UK T: +44 (0) LEEDS Suite 1, Jason House, Kerry Hill, Horsforth, Leeds LS18 4JR, UK T: +44 (0) LONDON 83 Victoria Street, London, SW1H 0HW, UK T: +44 (0) MAIDSTONE 19 Hollingworth Court, Turkey Mill, Maidstone, Kent ME14 5PP, UK T: +44 (0) MANCHESTER 8 th Floor, Quay West, MediaCityUK, Trafford Wharf Road, Manchester M17 1HH, UK T: +44 (0) NEWCASTLE UPON TYNE Sailors Bethel, Horatio Street, Newcastle-upon-Tyne NE1 2PE, UK T: +44 (0) NOTTINGHAM Aspect House, Aspect Business Park, Bennerley Road, Nottingham NG6 8WR, UK T: +44 (0) SHEFFIELD Unit 2 Newton Business Centre, Thorncliffe Park Estate, Newton Chambers Road, Chapeltown, Sheffield S35 2PW, UK T: +44 (0) SHREWSBURY 2 nd Floor, Hermes House, Oxon Business Park, Shrewsbury SY3 5HJ, UK T: +44 (0) STAFFORD 8 Parker Court, Staffordshire Technology Park, Beaconside, Stafford ST18 0WP, UK T: +44 (0) STIRLING No. 68 Stirling Business Centre, Wellgreen, Stirling FK8 2DZ, UK T: +44 (0) WORCESTER Suite 5, Brindley Court, Gresley Road, Shire Business Park, Worcester WR4 9FD, UK T: +44 (0)