Species Action Plans

Reed Warbler
Sedge Warbler
Water Vole
Amphibia
Common Hawker
Redshank
Kingfisher
Sand Martin
Lapwing
Kestrel
Grey Partridge
Skylark
Brown Hare

 


 

 

 


Water Vole
(Arvicola terrestris)

Habitat
Freshwater ponds
Ditches
Reedbeds

Water Vole on the Greatham Site
The accompanying map (PDF) shows the areas on site populated by Water Vole. Some of the ponds and ditches have breeding, resident, Water Vole, whereas others are suitable for Water Vole but have non-resident individuals or no individuals. Some of the ponds and ditches on site are unsuitable for Water vole, as they are saline. One of the ditches on site has been highlighted as an area for possible improvement, as the habitat is suitable but there are currently no Water Voles using it.

Status in UK and Europe
Water Vole are widespread in Britain but there is a serious decline in numbers and distribution. The British population is estimated at 1,200,000 animals.

Local Status
Under-recorded. Known on Marton West Beck and Coatham Marsh NR. Breeding on Greenabella Marsh.

Objectives for Water Vole on the Greatham Site

  • Assess the current level of Water Vole on the Greatham site.
  • Improve water Vole habitat in certain areas.
  • Extend the range of Water Vole over the site.

Management Plan for Water Vole on the Greatham Site

  • Continue monitoring of Water Vole on site, to assess the current distribution, and to highlight any increases in distribution on site.
  • Undertake habitat management to ensure that suitable habitat which is currently un-used by Water Vole, can be made more readily usable, to increase the distribution of Water Vole across the site.
  • The following management ideas were suggested by Physalia, and would hopefully achieve the above objective of increasing the distribution of Water Vole across the site:
    • Shallow earthen weirs with drain pipes installed through them, to prevent over-topping, placed in some of the overgrown drains to raise the water levels. The increase in open water would favour voles and extend existing ‘vole corridors’.
    • Controlled /managed clearing of overgrown sections of existing drains, with selective removal of vigorous, dominant plant species e.g. Typha latifolia. This is particularly important for the northernmost drain on the site, which has been marked ‘area for possible improvement’ on the accompanying map (PDF).
    • Selective planting of native willow species (local Salix alba and S. fragilis varieties) along the margins of some of the water bodies. This simple measure stabilises banks for vole burrows. More importantly, annual pollarding, close to ground level, provides a ready supply of new willow bark. This can be an invaluable food source for over-wintering vole populations and would directly reduce winter mortality.