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Ecological Site Briefings Minerals Site Options Detailed

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Ecological Site Briefings Minerals Site Options Detailed Wiltshire and Swindon Aggregate Minerals Site Allocations DPD Further assessment for Aggregate Minerals Site Options in Wiltshire and Swindon: Ecological Site Briefings Contents Introduction 1 Site Briefings 4 Site Option U2 4 Site Option U3 5 Site Option U4 6 Site Option U5 7 Site Option U6 8 Site Option U7 8 Site Option U9 9 Site Option U16 10 Site Option U17 11 Site Option U18 12 Site Option U22 13 Site Option U23 14 Site Option C3 15 Site Option C15 16 Site Option C16 17 Site Option C18 18 Site Option SE1 – SE3 19 Site Option SA1 20 Site Option SA2 21 Site Option BA4 22 Appendix A: Test of Likely Significance 23 SA1 25 SA2 30 SE1 – SE3 35 U7 41 U9 46 U22 52 1. Introduction This document aims to set out the relevant ecological issues for each minerals site in order to fully inform the planning process of the necessary processes that should be followed to ensure protection of the ecological integrity within each site. This document also addresses possible opportunities for enhancement in line with the requirements of Planning Policy Statement 9 (PPS9). Planning Obligations For most of the sites the ecology can be sufficiently addressed at the planning application stage in line with Planning Policy Statement 9: Biodiversity and Geological Conservation (PPS9), which will ensure no adverse impacts on protected species or sites and will require some habitat enhancement appropriate to existing site ecology. There is no guarantee that all the sites will come forward for planning approval as the process is landowner and developer led, therefore no habitat survey work by consultants is necessary until the planning application for each site is being prepared. It will be the responsibility of developers to engage suitably qualified consultant ecologists to survey their site in order to produce a report that will inform the planning application. Notwithstanding this, the County Ecologist has reviewed the existing data for each site against the current ecology within and immediately surrounding each site. Table 1 below sets out the ecological constraints for each site and the requirement for habitat and species survey to inform the planning process. Advice is also offered on appropriate restoration proposals and any constraints or specific requirements that would be relevant to those proposals. Most mineral sites are very large in area and their restoration can offer opportunities to replace, create and enhance areas of semi natural habitat at a landscape scale. As a general rule, all restoration proposals should aim to meet targets laid out in the Wiltshire Biodiversity Action Plan, for named species that are currently within the site or in adjacent areas, thus satisfying the requirement under PPS9 to deliver suitable enhancement for biodiversity through the planning system. Where mineral extraction sites are located within the Cotswold Water Park, there will be an additional requirement for restoration proposals to meet targets in the Cotswold Water Park Biodiversity Action Plan and to fall in line with the CWP BAP's Head of the Thames Vision, of which restored mineral sites have the opportunity to deliver a significant part. The long term nature of mineral extraction operations can result in large areas of natural and semi natural habitat being disturbed at any one time, potentially leading to deleterious effects on some faunal and floral species if they are unable to return in the short term. Where more than one operational mineral extraction site occurs adjacently or nearby, the effect can be cumulative. It is likely to be a requirement of any planning permission for mineral extraction that a construction method statement will be submitted as part of the application, detailing how provision will be maintained for wildlife to utilise key habitat areas within and around the site. A programme of phased working will be favoured, where restoration of early extraction phases is carried out alongside later extraction phases, to avoid the existence of large areas devoid of vegetation and thus help to lessen the impacts on the biodiversity of the area. The programme of phasing should ideally include a management plan for natural habitats to ensure that sufficient and appropriate habitat can be maintained for wildlife species throughout the operation and restoration of the site. 1 Statutory European Designated Sites The Core Strategy Habitats Regulation Assessment (HRA) document for the Wiltshire & Swindon Minerals and Waste Development Framework, carried out by Enfusion/C4S in July 2008 determined the predicted impacts of mineral site operation on the features of each European designated site, based on the sensitivities of those features as documented in the site information given by the Joint Nature Conservancy Council. (This information is given in Appendix 4 of the Habitats Regulations Assessment for the Minerals and Waste Core Strategies & Development Control Policies: Submission Reports July 2008). The predicted impacts cover the range of activities associated with all stages of mineral winning and working, from site preparation, through extraction, restoration and finally afteruse For each European site, the HRA concludes a distance below which it cannot be certain that a likely significant effect will not result from the operation of a mineral site. Six of the proposed mineral sites are located close enough to a European designated site to require a “test of likely significance” to determine whether or not the proposal could be likely to have a significant adverse effect on the designated features of the site. The pro forma for each of these six sites is shown in Appendix 1 – Habitats Regulations Test of Likely Significance. River Avon SAC SA1 – Land at Petersfinger, Salisbury SA2 – Land near Alderbury Farm, Salisbury North Meadow & Clattinger Farm SAC U7 – Land east of Calcutt U9 – Land near Latton U22 – Land west of Cotswold Community New Forest SAC SE1, SE2, SE3 – Land at Whiteparish Other Statutory Designated Sites In many cases the boundaries of Sites of Special Scientific Interest (SSSIs) are contiguous with the boundaries of European Sites for which they act as a management tool, although the designated features may vary between the SSSIs and European Sites. Some statutory designations are SSSI only and not associated with any European Site. Of these, some are designated for their biological features, e.g. Savernake Forest, while others are designated for their geological features, e.g. Stanton St Quintin Geological SSSI. Whether designated for their biological or their geological interest, the statutory legislation requires due regard is exercised in respect of those features. By their nature the geological SSSIs are often likely to be on previously quarried areas and often also adjacent to extant extraction permissions. Although not the qualifying feature for these SSSIs they are often hotspots for biodiversity, providing opportunities for a range of small mammals and invertebrates, bats, small native birds and also birds of prey. There is no standard distance from a SSSI at which it can be determined that impact is likely as this is very subjective, depending on the designated features of the SSSI, the possible impacts from operating the mineral site and whether there is any mechanism for impact such as hydrological connectivity or direction of prevailing wind in relation to both sites. Each site will require assessment of its individual issues at the planning application stage. The specific details of the requirements for survey and possible mitigation in respect of SSSIs are given in Table 1 below, in respect of each potential mineral site that may have the potential to impact on the designated features. 2 Local Sites – County Wildlife Sites County Wildlife Sites (CWSs) are the network of local sites of non-statutory designation, selected for their habitat type and their function for biodiversity. They usually contain areas of Priority Habitat (defined under the UK Biodiversity Action Plan list of Priority Habitats) and are protected through planning policy and process by the implementation of PPS9. Where CWSs occur within or immediately adjacent to potential mineral sites, consideration should be given to avoidance and protection through buffering of these important local sites. Consultation should be sought with the County Ecologist and the Wildlife Sites Project Officer in relation to current condition of any CWS potentially likely to be affected by mineral extraction and the potential to enhance their condition through the planning process, as required under PPS9. Life of this advice The advice given in this document is valid for the life of the Wiltshire & Swindon Aggregate Minerals Site Allocations DPD. However, the specific ecology of individual sites will change over time and prospective developers are therefore advised to engage a suitably qualified consultant ecologist at an early stage in the planning process, to properly determine the ecology of their site so that sufficient and appropriate mitigation and enhancement can be designed that will ensure no adverse effects on biodiversity as a result of development of the site. Sites with this symbol have been subject to a test of likely significant effect on a nearby European site, undertaken by the County Ecologist, as detailed in Appendix A of this report. 3 2. Site Briefings The following tables give a brief overview of the existing ecology of each potential site allocation, together with any constraints that may affect future proposed mineral developments. The evidence base for this table is drawn from existing records held at the Wiltshire & Swindon Biological Records Centre (WSBRC), Natural England site boundaries of SSSIs and European statutory designated sites and a comprehensive programme of site visits by the County Ecologist. It is intended to inform potential developers and planning officers of the likely ecological issues at individual sites that will need to be addressed in order to develop sites with due regard to biodiversity and to indicate appropriate enhancement that will benefit biodiversity in line with Planning Policy Statement 9 (PPS9).
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