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Case Example 17 – Drayton Quarries
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(C) English Nature
Site name: Drayton Quarries
Location: South-east of Chichester in West Sussex
Operator/owner: Tarmac plc
Local BAP: Sussex Biodiversity Action Plan
BAP habitats:
  • Reedbed
  • Wet woodland
  • Open standing water
  • Unimproved neutral grassland
  • Ancient and/or species rich hedgerows
  • Broadleaved woodland
  • Natural area: Low Weald and Pevensey


    Background and site description

    The Drayton sand and gravel quarries lie to the south-east of Chichester in West Sussex. The northern quarry is already worked for its aggregates by Tarmac plc, while the southern section is a new extension to the site.

    The original land-use at Drayton South, prior to mineral extraction, was intensive arable farming and ecological surveys of the site found it to be of minimal wildlife value. Instead of returning the land to agricultural use, the Mineral Planning Authority and Tarmac plc agreed a restoration scheme to habitats of high nature conservation value.

    The total area of the two quarries is in the region of 30 hectares, divided into approximately 13ha at Drayton North and around 17ha at Drayton South. Of the southern extension, nearly 12ha will be worked and a buffer of 5-10m will remain unworked around the periphery of the site, amounting to about 5ha in total.

    Initiative

    Sand and gravel extraction from Drayton South is taking place over a 3-4 year period in three phases of 12-15 months each, with a progressive restoration scheme implemented as soon as each phase of quarrying is finished. The quarry is worked wet, so no de-watering is necessary over the active phase of the site.

    Before extraction began, an advanced tree and shrub planting programme was undertaken to enhance an existing, gappy hedgerow, plant a new hedgerow, and create an avenue of oak trees along the track that separates the two halves of the site.

    The restoration scheme for Drayton South is based around an extensive freshwater lake with areas of reedbed, surrounded by a mosaic of species rich grassland and woodland. This scheme will complement the proposed restoration of Drayton North, which will be to a similar suite of habitats.

    The main elements of the restored Drayton South quarry are:

    • a freshwater lake of approximately 11.5 ha with scalloped, graded margins, reedbeds, shallows, deep pools, gravel beaches and islands
    • 2.3 ha of grassland margins, including a series of seasonal wetlands, scrapes and shallow ponds
    • 1 ha of woodland and scub, comprising 0.5 ha of broadleaved woodland, 0.1 ha scrub, and 0.4 ha of willow carr/wet woodland
    • additional features such as tern rafts, bird nesting boxes and bat boxes will be incorporated into the restored site.

    Costs

    Nature conservation does not incur any cost in addition to that of general site management and restoration.

    Benefits

    The Drayton South Quarry restoration scheme has taken account of both national and local BAPs and is intended to contribute to the following:

    Habitat Action Plans

    Species Action Plans

    Contribution to biodiversity
    The Lake

    The lake will be the main feature of the restored site. It will be primarily groundwater fed with some surface water input, and the natural hydrological movement through the site will be maintained by retaining uncovered gravel beaches above and below the waterline on the north and south lake margins. This will allow an unimpeded flow of groundwater across the site.

    The lake will have a variety of features to benefit different kinds of wildlife, including some muddy margins often favoured by invertebrates, as well as gravel beaches that are attractive to birds such as little ringed plover. There will be shallows where water is warmer and aquatic plants can colonise, deeper areas for diving birds, islands safe from predators, and tern rafts for nesting birds. Diverse, scalloped margins with spits and inlets of varied height, depth and gradient will further increase the value of the lake to fauna and flora.

    The reedbeds will be partially planted to about 20 per cent cover with the rest of the area left to natural colonisation. The scrapes and shallow ponds will be planted with appropriate native wetland plant species such as water mint and water forget-me-not. Native stock will be used for all the planting on the site, where possible using locally sourced material.

    The larger of the islands in the lake will not only have value to wildlife but will also protect an area of archaeological interest. The island outcrop will be excluded from extraction, as will a second area of archaeological value on the shore of the lake.

    Grassland

    The grassland fringe around the lake will be seeded using an appropriate mixture of native, local provenance wildflower and grass seed. It will be managed to promote a mosaic of micro-habitats including bare ground, short sward, dense tussocks, rank grassland and scrub leading from the waterline to the wooded areas.

    Grassland management will be by a varied mowing regime, with removal of cut material to maintain low soil fertility. Some control of pernicious weed species such as creeping thistle, ragwort and dock that might occur as a legacy of the former land use may be necessary.

    Woodland

    A mixture of appropriate species of native trees and shrubs such as oak, ash, hawthorn, hazel and field maple, if possible of local provenance, will be planted around the site margins to create areas of woodland with scalloped edges that grade into the scrub and grassland mosaic.

    Native black poplar will be used as a component of the wet woodland along with willows and alder.

    Soils

    Some of the topsoil from the site will be used in the restoration works, for example on the lake margins in places where reedbed is planned. Because of the progressive restoration of the site, topsoil and subsoil stripped from an area to be worked can be replaced immediately on parts of the previously extracted phase, which will minimise possible degradation of soils through unnecessary storage and handling. The lower fertility topsoil and subsoil will be used in the proposed grassland areas because limited soil fertility is more conducive to the development of species rich grassland and there is likely to be a heavy weed seed bank in the most fertile topsoil.

    Aftercare period

    A particularly important feature of the restoration scheme is the agreed 10-year aftercare period (rather than the usual five-year period).

    Tarmac plc plans to hold annual aftercare meetings throughout the 10-year aftercare period with the Mineral Planning Authority and with all parties with a legal interest in the site to inspect and review the restoration and aftercare progress.

    Photography
    During mineral extraction

    17-1.jpg - 6760 Bytes

    After mineral extraction

    Contact
    Tarmac plc

    Stuart Goldthorpe
    Tarmac Southern
    Lower Farm Quarry
    Hambridge Lane
    Newbury
    Berkshire
    RG14 5SS
      West Sussex County Council

    Brian Johnson
    Senior Mineral Planner
    County Hall
    West Street
    Chichester
    West Sussex
    PO19 1RQ

    Stuart.Goldthorpe@tarmac.co.uk

    Brian.Johnson@westsussex.gov.uk

    07702 632795 01423 756867

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