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Securing Biodiversity in Breckland - European Commission

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edstraw Galium parisiense (Tansley and Watt, undated). We do not know of a s<strong>in</strong>gle localityrema<strong>in</strong><strong>in</strong>g <strong>in</strong> <strong>Breckland</strong> where such an assemblage could be found today.From these <strong>in</strong>dependent l<strong>in</strong>es of qualitative evidence, it is likely that many species that depend onphysically disturbed and grazed conditions and a cont<strong>in</strong>uous supply of bare sand or chalky soil, willhave suffered severe and profound decl<strong>in</strong>es <strong>in</strong> their extent and abundance.Recognis<strong>in</strong>g Changes <strong>in</strong> Vegetation Over Time: an Example of Grass-Heath VegetationRodwell (1992) analysed samples of CG7b (the Cladonia spp. Sub-community of Festuca ov<strong>in</strong>a-Hieracium pilosella-Thymus praecox/pulegoides grassland Table 3, classified by Watt as his ‘grasslandB’) obta<strong>in</strong>ed <strong>in</strong> the mid 1970s. Rodwell commented on marked changes s<strong>in</strong>ce Watt’s time (e.g. Watt1940, 1957). Notably, Rodwell commented that “the vegetation is now generally grassier” withapparently greater amounts of more mesic grass species such as Holcus lanatus and Trisetumflavescens as well as mesic herbs such as Trifolium repens. Second, Rodwell commented that thetherophytes (small annual plants that require small scale disturbance and open swards, for exampleparsley-piert Aphanes arvensis, early forget-me-not Myosotis ramosissima, wall speedwell Veronicaarvesnsis, annual pearlwort Sag<strong>in</strong>a apetala, shepherds cress Teesdalia nudicaulis and spr<strong>in</strong>gspeedwell Veronica verna) were “now apparently much rarer”. This situation is compatible with areduction <strong>in</strong> the frequency of small scale disturbance, most likely due to a reduction <strong>in</strong> rabbitpopulations, and also with an accumulation of nutrients and/or closed matted swards. However, thesamples analysed by Rodwell also showed “marked reductions <strong>in</strong> the frequency and variety ofbryophytes and lichens” (Rodwell 1992). This is compatible with both a decrease <strong>in</strong> graz<strong>in</strong>g <strong>in</strong>tensityand an <strong>in</strong>crease <strong>in</strong> nutrient status.Rodwell did note caution <strong>in</strong> <strong>in</strong>terpret<strong>in</strong>g too much from a s<strong>in</strong>gle snapshot <strong>in</strong> time – however, it isnotable that these data were collected <strong>in</strong> the drought year of 1976 which would have hit mesicspecies hard and would not expla<strong>in</strong> a reduction <strong>in</strong> lichens (although annuals may have been crispedup and hard to detect by summer).There seems to be a consistent and cont<strong>in</strong>u<strong>in</strong>g pattern of deterioration of the grass-heath resource,as shown by measured change and perception of change across successive periods. This hascont<strong>in</strong>ued <strong>in</strong> the last 20 years despite the restoration of livestock graz<strong>in</strong>g across most grass-heaths.The evidence is summarised below.111

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