Purpose
The purpose of this guidance is to help NatureScot staff provide developers, planning authorities and Scottish Government with consistent advice on the effect of wind farms and other renewable energy proposals on peatland habitat. The guidance also sets out the framework within which NatureScot will decide when wind farms and other renewable energy proposals sited on peat raise natural heritage issues of national interest.
Introduction
The guidance describes how we will support the implementation of Scottish Planning Policy (2014) in relation to carbon-rich soils, deep peat and priority peatland habitat and onshore wind development. We will apply the same approach to all other forms of development.
Our approach aims to:
- encourage development to avoid carbon-rich soils, deep peat and priority peatland habitat and to minimise losses of the highest quality peatland habitat;
- help to mitigate any effects of development on carbon-rich soils, deep peat and priority peatland habitat; and
- ensure no net loss of public benefit through effective restoration and management of damaged bog to compensate for any losses.
Further guidance relevant to developments on peatland is contained in Annex 1.
Policy context
Scottish Planning Policy (SPP) establishes carbon-rich soils, deep peat and priority peatland habitat as nationally important environmental interests:
“Recognising the need for significant protection, in these areas wind farms may be appropriate in some circumstances. Further consideration will be required to demonstrate that any significant effects on the qualities of these areas can be substantially overcome by siting, design or other mitigation” (SPP, Table 1, page 39).
SPP (paragraph 161) requires planning authorities to embody this in spatial frameworks that identify those areas that are likely to be most appropriate for onshore wind farms. We have provided guidance for planning authorities on how to do this in Spatial Planning for Onshore Wind Turbines.
A more detailed and exacting development management process complements the spatial framework (paragraph 163) and paragraph 169 states:
“Proposals for energy infrastructure developments should always take account of spatial frameworks for wind farms and heat maps where these are relevant. Considerations will vary relative to the scale of the proposal and area characteristics but are likely to include (amongst others):
- effect on greenhouse gas emissions;
- impacts on carbon-rich soils, using the carbon calculator; and
- effects on the natural heritage”.
The National Peatland Plan, the 2020 Challenge for Scotland's Biodiversity and its associated Route Map, the Scottish Land Use Strategy and the Scottish Soil Framework all complement and support the intention of SPP with regard to carbon-rich soils, deep peat and priority peatland habitat and highlight the importance of these resources.
What are carbon-rich soils, deep peat and priority peatland habitats?
Carbon-rich soils are those with any surface organic (peaty or peat) layer. Peat in the Scottish soil classification is soil with more than 60% organic carbon and exceeding 50cm in thickness. The four peat forming priority peatland habitats defined in the UKBAP are: Blanket Bog, Lowland Raised Bog, Lowland Fens and part of Upland Flushes, Fens and Swamps.
Our Carbon and Peatland Map, published in June 2016, is available on Geo View (Carbon and Peatland 2016 layer) and on Scotland’s soils website which provides detail on how to interpret the map. It identifies the nationally important resource and enables planning authorities to map carbon-rich soils, deep peat and priority peatland habitat in a consistent manner in wind farm spatial frameworks.
The map is a strategic planning tool. It is not a definitive account of where important carbon rich soils, deep peat and priority peatland habitat exist. Development proposals on peat, whether in the mapped area or not, will always require a site-specific and detailed peat and vegetation survey to confirm the quality and distribution of peatland across the site. This information will confirm the extent to which nationally-important peatland will actually be affected by the development, and inform design, micro-siting and mitigation.
When responding to scoping requests we may note whether the proposal is within the mapped area, but we should focus our advice on the actual effects on peatland habitat.
Assessing the impacts of development on carbon-rich soils, deep peat and peatland
SPP affords ‘significant protection’ to carbon-rich soils, deep peat and priority peatland habitat and further consideration will be required to demonstrate that any significant effects on the qualities of these areas can be substantially overcome by siting, design or other mitigation (SPP, Table 1, page 39).
Assessing effects
Wind farms and other developments may have ‘direct’ or ‘indirect’ effects on peat.
- Direct impacts comprise a loss of peatland habitat from the development ‘footprint’ and habitat lost or damaged during construction and operation e.g. due to storage of topsoil/peat on habitat.
- Indirect impacts comprise impacts from either temporary or permanent changes in drainage patterns and the quality or quantity of surface and ground water. Peatland habitats are complex hydrological systems, vulnerable to activities occurring beyond the boundaries of individual habitat patches. Examples of indirect impacts include:
- down-slope droughting or up-slope flooding of peat-based habitat;
- the pollution of wetland habitat through accidental spillage of vehicular fuels and oils, and from the deterioration of track surfaces during their usage;
- reduced stability of peat-based habitat on steep slopes, which in turn may have further impacts on habitat and species should a peat slide event occur.
Determining when effects are significant
Carbon-rich soils, deep peat and priority peatland habitat are in Group 2 of Table 1 in SPP and afforded the same protection (with regard to wind farms) as Natura sites, SSSI and other international and national designations.
A ‘significant effect’ on the qualities of the carbon-rich soils, deep peat and priority peatland habitat is likely to result from:
- The complete loss of the resource (for example by excavation, or by covering the area in concrete)
- The loss of function of the habitat, whereby the peat, or peatland habitat, is likely to be lost or significantly degraded as a result of the development.
When a proposal will have significant effects we should advise of this in our response to the application. We should also recommend whether further mitigation is required. However, we will only use an objection when these effects are on peatland habitat which is deemed to be of national interest (see below).
How to respond
Avoidance
The benefits from avoiding areas of good peatland habitat include:
- reduced technical challenges and costs of constructing on deeper peat;
- reduced impact of peat excavation on carbon payback;
- less difficulty of managing excavated peat on construction sites;
- less need for identifying suitable uses for excavated peat.
Our role is to help developers avoid sensitive peatland habitat by designing an appropriate wind farm of the right scale for the site.
Mitigation
Impacts on peatland can be reduced by:
- conducting detailed habitat surveys and peat depth surveys;
- avoiding deeper peat and sensitive habitat;
- adopting alternative construction techniques such as floating roads and piled turbine foundations; and
- carefully planning drainage on the site and ensuring good maintenance of mitigation measures on site.
Compensation: habitat management and enhancement
When potential impacts cannot be avoided or mitigated (for example, through alterations to the site layout or construction techniques), it is good practice to identify opportunities for habitat enhancement. This seeks to improve the condition of existing peatland habitat and to restore damaged habitat.
We should encourage developers to undertake habitat management and enhancement when peatland habitat is lost to development. In some circumstances, where we consider the likely loss of peatland habitat is of national interest, we should use a conditioned objection to ensure that any consent provides adequate compensation for any loss.
Typical compensation measures include:
- tree removal2
- blocking drains/installing dams;
- cessation of burning/peat cutting; and
- reducing grazing and trampling pressures.
Further guidance on habitat management plans is available. Guidance on peatland restoration is available.
Identifying when impacts may be of national interest
To help determine when a proposal could have a significant effect that is of national interest, we have developed a new assessment framework (see Annex 2 and site visit template). This framework starts from the position that national interest will only arise when peatland of the highest quality is lost or damaged. We want to:
- avoid any further loss of raised and montane bogs;
- minimise the loss of peat-forming blanket bog; and
- ensure no net loss of public benefit through effective restoration and management of damaged bog to compensate for any losses.
Our focus is on peatland habitat. We will not raise national interest matters solely on the carbon implications of new developments, or the impacts on ‘deep peat’.
The framework adopts elements of the criteria used to select SSSIs and uses information collated from the Environmental Statement (mainly in the Ecology chapter and the Geology and Hydrogeology chapter, together with supporting Appendices) complemented by information on GeoView, aerial photography and other relevant data and additional field observations.
Having applied the tests in Annex 2 and concluding that there are significant effects that cannot be substantially overcome, you should consider an objection in line with our National Interest Guidance. You should seek specialist advice from Habitats Group (Rural Resources Unit) and refer the case to the Area Manager if necessary.
Working with other agencies
When providing advice on the impacts of development on carbon rich soils, deep peat and priority peatland habitat, it is important that we work with other key agencies to align our advice.
- We should liaise with SEPA on issues relating to groundwater dependent terrestrial ecosystems (GWDTEs); hydrology; waste management (such as the treatment of peat excavated during construction) and carbon emissions.
- We should liaise with FCS where proposals for development, or peatland restoration, may result in woodland removal or have an effect on woodland resources.
Annex 3 shows the topics on which we and SEPA currently lead.
Annex 1. Further guidance
Title |
Description |
---|---|
Describes peat failure mechanisms and outlines the requirements for peat stability assessment. Aims to provide guidance on the best methods for identifying, mitigating and managing peat slide hazards and their associated risks. |
|
SEPA (2010) Regulatory Position Statement - Developments on Peat |
Explains SEPA’s position regarding re-use and disposal of peat excavated during developments. |
JNCC (2010) Handbook for Phase 1 Habitat Survey: a technique for environmental audit |
Presents a standardised system for planning and undertaking habitat surveys and classifying and mapping wildlife habitat. |
Provides guidance for the ecological impact assessment (EcIA) of all types of development in terrestrial, coastal and freshwater environments. Sets out widely accepted good practice for each stage of the EcIA. |
|
Guidance On The Assessment Of Peat Volumes, Reuse Of Excavated Peat And The Minimisation Of Waste |
This document is aimed at businesses engaged in activities that involve developments on peat. It applies to all forms of development on peat, although the examples used are taken from wind farms. |
This guidance provides key principles for surveying peatland for a wide range of applications such as: Peat landslide risk assessments |
|
This provides further information on the key species identified in Annex 2. Sphagnum austinii - NBN - BBS |
Annex 2. Assessing the likely impact of renewable energy development on peatland and determining when this may be of national interest
Case Officers should always complete the assessment set out in this Annex before seeking specialist advice. This will help them determine whether specialist advice is needed and inform the specialist assessment. Please use the site visit template.
Assessment criteria for each proposed infrastructure mentioned in the ES.
- Raised Bog supporting ‘typical’ bog vegetation.
Yes: Likely National Interest
- Montane Bog supporting ‘typical’ bog vegetation.
Yes: Possible National Interest
3. Blanket Bog - based on quality criteria used in identifying potential SSSI.
A. Is the proposed development within a continuous unit of blanket bog >25ha?
Yes: Go to B
No: Advise on mitigation measures
B. Does the proposed development and/or the wider area of blanket bog of which it is a part, support vegetation capable of forming peat?
Yes: Go to C
No: Advise on mitigation measures
C. Does the proposed development footprint (with a buffer of 250m) support two or more of the following?
- Low frequency of drains and peat cutting
- Presence of plant species indicating peat formation capability and/or lack of disturbance
- An area of natural surface pattern
- Absence of invasion by woodland or scrub
Yes: Possible National Interest
Consult adviser
No: Go to D
D. Does the proposed development footprint support one or more of the following?
- An abundance of Sphagnum-rich ridges
- Ridges of Sphagnum - Betula nana
- Hummocks of S.fuscum or S. austinii
- Peat mounds
- Hollows of Sphagnum or bare peat - Rhynchospora fusca
Yes: Possible National Interest
Consult Habitats Group
No: Advise on mitigation measures
Annex 3. NatureScot and SEPA roles in relation to carbon rich soils, deep peat and priority peatland habitat.
NatureScot | SEPA |
---|---|
Groundwater Dependent Terrestrial Ecosystems (GWDTEs) which are the qualifying interest of protected areas, or which could affect the qualifying interest of protected areas. |
Groundwater Dependent Terrestrial Ecosystems in the wider countryside, or within protected areas but not a qualifying interest. |
Peat landslide risk assessments, where the risks could affect protected areas or areas of carbon-rich soils, deep peat and priority peatland habitat. |
Peat landslide risk assessments where these could affect the water environment, or are relevant to one of the other SEPA interests on this table (e.g. could be relevant to consideration of impact on GWDTEs). |
UKBAP priority peatland habitat. |
Fens (which are GWDTEs), outwith protected areas. |
Carbon-rich soils, deep peat and priority peatland habitat map. |
Peat re-use and waste management. |
Habitat Management Plans, Peat Management Plans, Construction Method Statement or Construction Environmental Management Plans where these are required to mitigate effects on one of the other NatureScot interests listed on this table (i.e. a protected area, UKBAP priority peatland habitat). |
Habitat Management Plans, Peat Management Plans, Construction Method Statement or Construction Environmental Management Plans where these are required to mitigate effects on one of the SEPA interests listed in this table (i.e. GWDTE, the water environment, waste management etc.). |
Footnotes
1. See Control of woodland removal policy and refer to FCS