Lowland Heathland - SW
LBAP Home Habitats Common themes

Cornwall

Devon

Dartmoor

Gloucestershire

Purbeck

Taunton

W Somerset

       
Key factors
 SW Resource Breakdown:2

County SW Resource
Avon 0%
Cornwall 46%
Devon 16%
Dorset 35%
Glouc. 0%
Somerset 2%
Wilts. 0%

1Action for biodiversity
in the South West (1997)

2SW Biodiversity Audit (1996)


Current Status in the SW

Definition1

Definition: Open, uncultivated nutrient-poor (usually below 250m); dominated by ericaceous heather and gorse


Current Extent1

The South West contains a significant proportion of the remaining UK lowland heathland resource. The region has some 14,500 ha which represents 25% of the UK total (c58,000 ha). The figure for the South West includes both wet and dry heaths, coastal heaths, and associated flush & mire systems. Southern Atlantic wet heaths with Erica ciliaris and Erica tetralix and all dry heaths are listed in Annex I of the EC Species and Habitats Directive.

Examples of important sites in the South West1

  • Carrine Common (Cornwall)
  • The Lizard (Cornwall)
  • West Penwith Moors (Cornwall)
  • East Devon pebblebeds (Devon)
  • The Dorset Heaths (Dorset)
  • Isles of Scilly Coastal Heaths (Isles of Scilly)
  • Exmoor Coastal Heaths (Somerset & Devon)
  • New Forest (Wiltshire/Hants)

 


Habitat Loss1

Loss of habitat has occurred on most of the main heathland blocks in the South West over the last 200 years, particularly to agricultural improvement and afforestation.

Associated Species1

Birds

  • Nightjar
  • Woodlark
  • Dartford Warbler
  • Stonechat

Reptiles

  • Sand Lizard
  • Smooth Snake

Invertebrates

  • Silver-studded blue
  • Grayling (Butterfly)
  • Speckled Footman
  • Large Marsh Grasshopper
  • Heath Grasshopper
  • Southern Damselfly
  • Ladybird Spider
  • Narrow-headed ant
  • Black Bog Ant

Plants

  • Heather
  • Bell Heather
  • Dorset Heath
  • Cornish Heath
  • Heath Lobelia
  • Western Gorse
  • Marsh Gentian
  • Pale Butterwort
  • Sundews
  • Marsh Clubmoss



Current factors affecting the habitat in the SW

  • Neglect and scrub encroachment.
  • Agricultural improvement (Devon & Cornwall).
  • Inappropriate management including unsuitable burning and levels of grazing.
  • Development, especially for roads, minerals, housing and associated infrastructure.
  • Recreational pressures and lack of public awareness.
  • Lack of protective designations of areas of potential heathland (currently under other land uses, which are on soils that are capable of supporting heathland.
  • Danger of heath fires as summers become potentially hotter and drier.

UK biodiversity objectives and proposed targets

UK Lowland Heathland Costed Habitat Action Plan:

Maintain, and improve by management, all existing lowland heathland (58,000 ha)

Encourage the re-establishment by 2005 of a further 6,000 ha of heathland with the emphasis on the counties of Hampshire, Cornwall, Dorset, Surrey, Devon, Staffordshire, Suffolk, Norfolk in England and Pembrokeshire, Glamorgan, West Gwynedd in Wales, particularly where the links separate heathland areas.


South-west biodiversity objectives and proposed targets

OBJECTIVE 1

Maintain the integrity of all existing heathland blocks through ensuring that they are protected from damage and loss

TARGET: ongoing

Lowland heathland is a rare and threatened habitat nationally, having suffered large scale losses in the last two centuries. The South West is a stronghold of this habitat in the UK. This reflects the UK target of maintaining all existing lowland heathland. Existing heathland must be protected from direct and indirect loss through statuary (e.g. site designation, protection and favorable management) and non-statutory means.


OBJECTIVE 2

Ensure that all heathland blocks are managed appropriately to restore and enhance biodiversity.

TARGET: by 2005

Neglect and inappropriate management have been identified as having an adverse effect on many sites. Countryside management schemes should be targeted to areas supporting lowland heathland and the funding should be at a sufficient level to encourage such management. Management must maintain a low nutrient ecosystem, which will in turn provide niches for dependent species, and aid regeneration of a diverse heathland vegetation structure. Restoration of degraded heathland on all sites/complexes in the region, particularly the key sites, is essential.

* Restoration in this context refers to the removal of invasive scrub, bracken and self-sown trees from heathland.


OBJECTIVE 3

Re-establish 3,500 ha of lowland heathland in the region, consolidating the existing major blocks/complexes.

TARGET: 2,000 ha by 2005, 3,500 ha by 2010.

The figure presented in this plan is based on those sites judged to have 'high' re-establishment potential and feasibility given resource and landownership constraints. Further work is required to identify and agree specific sites and areas for re-establishment*, but this plan gives an indication of the potential for delivery of the UK target in the region and to address part losses. A significant proportion of the UK target of an additional 6,000 ha can potentially be delivered in the Region. The timescale of 2010 is longer-term than that in the UK action plan, reflecting the timescale required in forward planning and implementation by relevant agencies.

* re-establishment is used in this HAP to refer to the establishment of open heathland from, for example, forestry plantation with or without heathland vegetation and seedbank present, grassland and arable land with or without seedbank, and where heathland has been lost through encroachment by invasive species. The term reflects the terminology of the lowland heathland habitat action plan set out in Biodiversity: The UK Steering Group Report. Re-establishment targets therefore refer to new/additional areas of heathland over and above those subject to restoration/scrub removal, as referred to in objective 2.


OBJECTIVE 4

Achieve an increase in community awareness and appreciation of heathlands and their conservation requirements in all key heathland complexes.

TARGET: by 2000

There is scope for more provision for better public appreciation of many sites. Public awareness is necessary for conservation work and priorities to be understood and supported, and may also reduce adverse effects of human use e.g. inappropriate recreational use, fires

 



Current Action

Some of the large sites in Dorset benefit from ownership by local authorities and NGOs, and from management by, for example, the RSPB Dorset Heathland Project, A large proportion of the East Devon pebblebeds is managed by the RSPB with co-operation from the landowners. Much of The Lizard is managed by the National Trust and English nature.

Management is funded through English Nature WES and RES schemes, MAFF Countryside Stewardship, and heathland re-establishment in Dorset by the National Trust. Stewardship target areas fro 1996/97 include heathland in:

Helston - St. Breock (Cornwall)
Greater Purbeck (Dorset)
Haldon (Devon)
Scilly

ESAs cover Dartmoor, Exmoor, Blackdowns and West Penwith, including approximately 2,775 ha of 'rough land' in West Penwith ESA, most of which is heathland, under agreement in 1995.

Individual strategies have been produced for some areas of heathland e.g. East Devon (Devon Wildlife Trust and East Devon District Council), Dorset (the Dorset Heathland Strategy produced by the Dorset Heathland Forum) and some provisions have been made in the Forest Enterprise Forest Design Plans e.g. in the Forest of Dean. Forest enterprise Forest design Plans e.g. in the Forest of Dean. Forest Enterprise is developing its own 'Endangered Habitats Plan' for lowland heathland and its ownership or control, which is due for completion this year.

Together the MoD and Herpetological Conservation Trust have recreated several areas of lowland heath in South Dorset (West Moors, Bovington and Lulworth) which has been of benefit to species such as sand lizard and southern damselfly.

Preliminary research into the feasibility of, and priorities for, heathland re-establishment has been undertaken for the main lowland heathland complexes of Dorset, Devon and Cornwall. In Dorset and Cornwall, English Nature has started to develop heathland 're-creation' plans. In Devon, the RSPB, Devon Wildlife trust and Devon County Council have co-operated to start to identify areas of heathland loss and where heathland re-establishment may be possible (further details on re-establishment are given at the end of this plan).



Policy and legislation

Review countryside management schemes to ensure appropriate prescriptions, adequate funding and uptake to achieve management, restoration and reestablishment (ongoing)

LEAD: MAFF, EN
PARTNERS: NGOs


Management


Ensure that safeguarding of all heathland through statutory of all heathland through statutory (county wildlife sites) recognition (by 1998)

LEAD: LAs
PARTNERS: EN, NGOs, DoE, DoT, MoD


Ensure safeguarding of all heathland through statutory (county wildlife site) recognition (by 1998)
LEAD:EN, DoE, LAs, WTs
PARTNERS: RSPB, HT


Ensure that appropriate countryside management schemes are targeted towards heathland management, restoration and re-establishment in the key areas identified in this HAP (by 2010)

LEAD: EN, MoD, LAs
PARTNERS: NGOs


Develop appropriate mechanism for funding for heathland management, restoration and re-establishment through UK government and/or EU (by 2000)

LEAD: DoE


Secure funding for heathland management, restoration, and re-establishment (ongoing)

LEAD: RSPB, WTs
PARTNERS: LAs, WTs


Ensure that site action plans include management restoration and re-establishment, and are agreed for all publicly owned sites (ongoing)

LEAD: EN, MoD
PARTNERS: NGOs


Facilitate issue of felling licenses for removal of trees from heathlands where future management can be ensured (by 2000)

LEAD: FA
PARTNERS: EN, DoE, LAs


Seek Lottery/Heritage funding for heathland management, restoration and re-creation including acquisition fro heath and landswap (by 2000)

LEAD: EN
PARTNERS: EN, NGOs, LAs, FE


Pursue acquisition of existing or potential heathland sites, particularly where management problems and opportunities exist or policy gains are not possible (use criteria given at the end of this plan: by 2000)

LEAD: NGOs, LAs
PARTNERS: FE, FA, EN, LOs



Liaise with forestry agencies, landowners and operators to seek to re-establish 3,500 ha of heathland in key areas, for example, through incorporating targets/actions in FDPs (2010)

LEAD: ALL
PARTNERS: MoD, LOs



Ensure that after-use of mineral workings within heathland areas enables heathland re-establishment (ongoing)

LEAD: LAs
PARTNERS: FE, NGOs, EN, MCos, DoE, EA


Advisory

Provide management advice to heathland landowners and managers (ongoing)

LEAD: RSPB, ADAS, EN
PARTNERS: LAs, WTs, HCT, NT, FWAG



Research and monitoring

Disseminate findings from research into management practice, techniques, impacts and problems (ongoing)

LEAD: EN, ITE
PARTNERS: RI, NGOs, DoE, ERCs


Ensure that monitoring of effects of heathland management techniques, and habitat and species surveys are co-ordinated throughout the region (by 1998)

LEAD: ALL
PARTNERS: DoE, LAs, BTO



Education and awareness raising


Ensure that heathland conservation messages are delivered at existing interpretation/education facilities (by 1998)

LEAD: LAs, EN, NT
PARTNERS: FE, FA, WTs, RSPB, HCT


Develop education/profile raising programmes at each key heathland complex.

LEAD: LAs, En, NGOs
PARTNERS: NFU, CLA, LOs


Benefits

  • Fulfilling the biodiversity objectives of this habitat action plan are likely to bring about a number of additional important benefits:
  • Landscape enhancement, often of cultural and historic significance
  • Conservation, and its needs, often results in large-scale government funding e.g. WES, CS, and EU funding (LIFE) being attracted into an area.
  • Providing a resource that has recreational and tourism benefits; in turn, this may also have important economic and rural development benefits.