Whitton Bridge Pasture is nationally important for its species-richgrassland which is unimproved by fertilisers. This type of grassland—once common in the Tees lowland—is becoming increasingly rare with its associated species also becoming scarce. Whitton Bridge Pasture is one of only two remaining examples of this habitat in the Tees lowland area. The other example is Briarcroft Pasture, an SSSI about 3 kilometres (1.9 mi) to the south, which was designated at the same time but is significantly smaller.[2][3]
Yorkshire Fog is one of the dominant species in subcommunity MG5c.
Located north-west of Stockton-on-Tees and 500 metres (550 yd) south of the village of Whitton, it is a small site of 3.18 hectares (7.9 acres) between a sewage works and Whitton Beck. Topographically the site slopes north towards the stream from a height of 40 metres (130 ft) to less than 30 metres (98 ft).[6] The underlying geology of Whitton Bridge Pasture is responsible for shaping the species-rich community found on the surface. Glacial tills and sands are the prominent geological features resulting in a relatively base-poor soil, characteristic of glacial drift geology. The soils of MG5c (Danthonia decumbens) subcommunity are typically acidic.[2][5]
Because Whitton Bridge Pasture is located in North East England it experiences a climate that is different from the UK average.[7] The North East receives on average 370 millimetres (15 in) less rainfall than the UK over a year. Similarly the North East has roughly 129 days each year with more than 1 millimetre (0.039 in) of rainfall, more than 25 days fewer than UK average. Despite these differences the temperature is similar for both the North East and the UK, although the North East does have fewer days with air frost and more hours of sunshine per year.[8][9]
Biotic
The majority of the site is made up of species-rich grassland (subcommunity MG5c), which comprises three dominant species of grass and several other grass species at lower abundances. The dominant species are Red Fescue (Festuca rubra), Common Bent (Agrostis capillaris) and Yorkshire Fog (Holcus lanatus). The less abundant species of grass include, Crested Dog's-tail (Cynosurus cristatus), Heath-grass (Danthonia decumbens) and Cocksfoot (Dactylis glomerata). The subcommunity also has many broad-leaved herbs including Common Knapweed (Centaurea nigra), Tormentil (Potentilla erecta), Devils-bit scabious (Succisa pratensis) and Betony (Stachys officinalis).[5]
A second subcommunity (MG5a) is present and is characterised by the legumeMeadow vetchling (Lathyrus pratensis). Other species present in this subcommunity include Salad burnet (Sanguisorba minor), Quaking grass (Briza media), Pignut (Conopodium majus) and the Orchid species: Common Twayblade (Neottia ovata) and Early Purple Orchid (Orchis mascula). The subcommunity also contains Meadow barley (Hordeum secalinum), a perennial grass, which is a characteristic species of the Tees Lowland.[5]
The two subcommunities of MG5, characterised by species rich grassland form a belt across the site, but they do not cover the whole site. Towards the north there is a community dominated by False oat-grass (Arrhenatherum elatius), a constant species in the MG1 and MG2 communities of the British NVC and therefore not typical of an MG5 community.[10] At Whitton Bridge Pasture it is growing on alluvial soils located at the northern edge of the site, which have most likely been formed by Whitton Beck just to the north. A number of springs at the site are associated with flushes of the Pale sedge (Carex pallescens), which form small populations.[5]
Management
Meadow vetchling is a characteristic species of subcommunity MG5c at Whitton Bridge Pasture.
Natural England's role is to advise and help the owners manage Whitton Bridge Pasture effectively. To achieve this Natural England provides guidelines for each SSSI. Species-rich grassland, such as that found at Whitton Bridge, requires careful management for it to retain its high species diversity. This means many activities are not allowed at the site including: ploughing, drainage and the use of fertilisers, pesticides or herbicides.[11][12]
Management of the site requires moderate grazing during the summer and autumn to help maintain the species diversity. This is because grazing removes each year's new growth which helps stop the site becoming dominated by vigorously growing grasses. Such grasses would allow a buildup of dead organic matter, which together with the increased growth, would reduce the growth of less vigorous species. The overall effect would be a reduction in species diversity, which was one of the reasons for the SSSI designation. Trampling can be of benefit because it breaks up accumulated dead organic matter.[13]
The small and isolated nature of the site makes it susceptible to damage from the surrounding area. For example, herbicides, thought to be generally damaging for the species richness, could get onto the site from the drift of spray from surrounding fields. To help combat this the maintenance of mature hedgerows around the perimeter is encouraged.[13] As of 2006 the condition of Whitton Bridge Pasture is described as favourable,[14] which means that the land is being adequately conserved and any conservation objectives are being met, but that there is scope for enhancement of the site.[15] The condition of the site was also described as favourable in 2004 and 2005 assessments.[3] In the future it is hoped that the grazing regime will become more regularised and will be of high priority.[16]
^John S. Rodwell, ed. (1998). British Plant Communities Volume 3: Grasslands and montane communities. Cambridge University Press. p. 63. ISBN0-521-62719-2.
^John S. Rodwell, ed. (1998). British Plant Communities Volume 3: Grasslands and montane communities. Cambridge University Press. p. 514. ISBN0-521-62719-2.
