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Securing Biodiversity in Breckland - European Commission

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the status of Deschampsia flexuosa. This plant is highly palatable to rabbits, and only two plants wererecorded before the war; today it is widespread and occurs as an abundant component of grassland"(Crompton 1971). A comprehensive and detailed report of vascular plants at Foxhole Heath preparedby S.M. Walters follow<strong>in</strong>g site visits <strong>in</strong> 1950 and 1953 (Tansley and Watt, undated) did not <strong>in</strong>cludeDeschampsia flexuosa; however <strong>in</strong> 1971 Eric Duffey noted a small patch of this grass “which I had notseen before dur<strong>in</strong>g the period we were there work<strong>in</strong>g on the fauna” (i.e. dur<strong>in</strong>g the mid 1950s).With<strong>in</strong> <strong>Breckland</strong>, D. flexuosa is particularly associated with sites where an organic horizon hasaccumulated overlay<strong>in</strong>g the m<strong>in</strong>eral sand. In contrast Festuca ov<strong>in</strong>a may occasionally be found closeto D. flexuosa dom<strong>in</strong>ated swards, but <strong>in</strong> patches reta<strong>in</strong><strong>in</strong>g m<strong>in</strong>eral soil with m<strong>in</strong>imal or no overly<strong>in</strong>gorganic material (e.g. on track verges with disturbance; P. Dolman pers. obs.). Thus, the <strong>in</strong>crease <strong>in</strong> D.flexuosa is compatible with reduced graz<strong>in</strong>g <strong>in</strong>tensity, the accumulation of nutrients through reducedmanagement and with the effects of nitrogen deposition.Pitcairn, Fowler and Grace (1991) quantified change <strong>in</strong> three <strong>Breckland</strong> heathlands (Cavenham,Knettishall, Tuddenham) and concluded that reductions <strong>in</strong> the cover of Calluna vulgaris was at leastpartly attributable to <strong>in</strong>creased nitrogen deposition. However, changes occurred over a period thatalso experienced greatly reduced graz<strong>in</strong>g pressure.For calcareous grass-heath vegetation <strong>in</strong> <strong>Breckland</strong> (e.g. CG7), changes <strong>in</strong> composition noted byRodwell by the 1970s (<strong>in</strong> contrast to the composition described by Watt <strong>in</strong> the 1940s and 1950s)<strong>in</strong>cluded a reduction <strong>in</strong> abundance and diversity of both bryophytes and lichens, an overall <strong>in</strong>crease<strong>in</strong> grass and an <strong>in</strong>crease <strong>in</strong> particular grass species that are more competitive with high levels ofnutrient availability or moisture, such as yellow oat-grass Trisetum flavescens and Yorkshire fogHolcus lanatus (Rodwell 1992). These changes are compatible with the effects of nitrogen deposition.Potential management techniques to mitigate effects of nitrogen depositionLegum<strong>in</strong>ous herbs <strong>in</strong>clud<strong>in</strong>g birds-foot trefoil Lotus corniculatus and black medic Medicago lupul<strong>in</strong>acan fix large volumes of nitrogen with<strong>in</strong> grassland ecosystems (e.g. 30-100 kg ha -1 yr- -1 , Marrs et al.1983), similar or greater than rates of nitrogen deposition. Wells et al. (1976) suggested that<strong>in</strong>tensive selective rabbit graz<strong>in</strong>g can effectively exclude nutritious legumes from the sward and thatthis was important <strong>in</strong> reduc<strong>in</strong>g nutrient accumulation <strong>in</strong> lichen rich CG7 vegetation on raw chalk soilsof the Porton Ranges, Wiltshire.In addition, it is highly likely that disturbance of vegetation and root mats by scrap<strong>in</strong>g and burrow<strong>in</strong>gby rabbits and the concentration of dung and ur<strong>in</strong>e <strong>in</strong> latr<strong>in</strong>e areas where vegetation is killed-off,both favour leach<strong>in</strong>g of volatilised nitrogen at least dur<strong>in</strong>g w<strong>in</strong>ter ra<strong>in</strong>fall. Thus rabbits may be key toma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g low nutrient status <strong>in</strong> grass-heaths. Schw<strong>in</strong>n<strong>in</strong>g and Parsons (1996) showed that nitrogenconcentrations <strong>in</strong> ur<strong>in</strong>e exceed the ability of grassland swards to utilise and capture the nitrogen,lead<strong>in</strong>g to losses through volatilisation and leach<strong>in</strong>g. However, experimental research quantify<strong>in</strong>gnitrogen budgets and fluxes <strong>in</strong> different grass-heath management systems is lack<strong>in</strong>g.Enhanced levels of graz<strong>in</strong>g to remove biomass can contribute to mitigation, but graz<strong>in</strong>g cannot <strong>in</strong>itself prevent deleterious changes <strong>in</strong> vegetation composition with enhanced nitrogen availability. Soildisturbance treatments <strong>in</strong>volv<strong>in</strong>g rotovat<strong>in</strong>g, plough<strong>in</strong>g, sub-soil<strong>in</strong>g, or turf stripp<strong>in</strong>g and removal ofsurface organic material, are probably the most effective ways of mitigat<strong>in</strong>g nitrogen deposition.101

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