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Securing Biodiversity in Breckland - European Commission

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Management to Susta<strong>in</strong> Dry Terrestrial AssemblagesIn this section we provide guidel<strong>in</strong>es for land managers to support and enhance the variousassemblages of priority species for conservation <strong>in</strong> <strong>Breckland</strong>. We also identify areas of uncerta<strong>in</strong>ty,recommendations for research and emphasise the need for monitor<strong>in</strong>g outcomes.An important priority must be to restore appropriate conditions for specialist assemblages of<strong>Breckland</strong> conservation priority species across the exist<strong>in</strong>g resource of designated sites, <strong>in</strong>clud<strong>in</strong>gboth statutory (SSSIs) and non-statutory (CWS). At many terrestrial sites, there is a lack of disturbedground with dom<strong>in</strong>ance by later successional stages. Many sites are managed by homogenousgraz<strong>in</strong>g regimes and would benefit from some heterogeneity of sward structures, creation of nectarresources and juxtaposition of ungrazed disturbed ground.Current approaches to grass-heath managementWe were able to compile habitat management questionnaire responses for a total of 2,446 ha of<strong>Breckland</strong> grass-heath, cover<strong>in</strong>g most key heath SSSIs. Of this area, all but 45 ha was grazed (98.2%grazed), with sheep used to graze all sites. Cattle were also present on areas of one large heathland.The <strong>in</strong>tensity of sheep graz<strong>in</strong>g varied between sites and compartments. While graz<strong>in</strong>g <strong>in</strong>tensity wasdescribed as moderate or high (e.g. Thetford Heath, c. 25 ewes ha -1 ) on many sites (compris<strong>in</strong>g 41%of the aggregate area), on 32% of the aggregate area sheep density was described as low or light (e.g.c0.7 ewes ha -1 , 0.8 ha -1 , 1.5 ha -1 and 2 ha -1 ). Graz<strong>in</strong>g density <strong>in</strong>formation was not obta<strong>in</strong>ed for therema<strong>in</strong><strong>in</strong>g area. Consider<strong>in</strong>g just the area for which sheep density was supplied, 57% was moderateto high, but 43% had low <strong>in</strong>tensity of graz<strong>in</strong>g.Rabbit population density was described as virtually absent to low on 57% of the total grass-heath,and as moderate to high for 25%. When just the sites for which we obta<strong>in</strong>ed rabbit <strong>in</strong>formation wereconsidered, 70% had no or very few rabbits.Qualitative assessment of the extent of bare ground was available from 95.5% of the area of grassheath.Bare ground was described as:very rare or rare: 52%occasional: 25%abundant : 19%Accurate <strong>in</strong>formation quantify<strong>in</strong>g the extent of physical disturbance treatments was available for 9SSSIs cover<strong>in</strong>g a total of 1387 ha. Across these, physical disturbance plots amounted to 11 ha, or0.8% of the area. It should be noted that these <strong>in</strong>clude key sites <strong>in</strong> which disturbance treatmentshave been pioneered and most widely applied. Thus, across the grass-heath conservation resourcephysical disturbance will amount to much less than 1%.In conclusion although some sites receive <strong>in</strong>tensive sheep graz<strong>in</strong>g, and some sites have rabbits, 43%of sheep grazed area was managed by low <strong>in</strong>tensity graz<strong>in</strong>g, 70% of the area extent had no or fewrabbits and disturbance treatments covered less than 1% of the grass-heath extent.147

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