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Securing Biodiversity in Breckland - European Commission

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Creat<strong>in</strong>g networks for resilienceTo reduce biodiversity losses from exist<strong>in</strong>g sites and to allow restoration and resilience ofpopulations for the longer term, opportunities should be taken to Restore and ensure cont<strong>in</strong>uity of appropriate conditions with<strong>in</strong> rema<strong>in</strong><strong>in</strong>g sites. Consolidate adjacent sites <strong>in</strong>to larger contiguous <strong>in</strong>tegrated units for management acrossland-ownership boundaries. This will <strong>in</strong>crease the potential size and resilience of speciespopulations, particularly of highly specialist species. Buffer and expand exist<strong>in</strong>g sites, where possible, so that conditions and populations aremore likely to be susta<strong>in</strong>ed with<strong>in</strong> them. Buffer<strong>in</strong>g of some heathland sites has beenachieved, for example at Weet<strong>in</strong>g and Cranwich and this approach should be extended wherepossible. Develop connectivity networks to enhance the resilience of sites and of the biodiversity theyprotect and to provide opportunities for dispersal and recolonisation.This needs a coord<strong>in</strong>ated and <strong>in</strong>tegrated strategic approach to conservation plann<strong>in</strong>g across sites,rather than just with<strong>in</strong>. It is the latter, <strong>in</strong>tra-site scale which currently dom<strong>in</strong>ates conservationactivity.Suggestions are made below on re-unit<strong>in</strong>g fragments that are either immediately adjacent, or locatednearby, and that could potentially be jo<strong>in</strong>ed <strong>in</strong>to larger contiguous complex units.Example of a potential networkThetford Heath once covered a wide sweep of landscape to the west, south-west and south ofThetford. It is now reduced <strong>in</strong> extent to Thetford Heaths SSSI, which exists as three potentiallycontiguous units that are under separate ownership and are currently fragmented and isolated by<strong>in</strong>terven<strong>in</strong>g woodland belts (see next page). The units <strong>in</strong>clude the unfavourable western unit 1(condition unfavourable no change), the core NNR (the only part currently <strong>in</strong> favourable condition),and the Eastern unit 3 (Barnham MOD camp <strong>in</strong> unfavourable recover<strong>in</strong>g condition). By removal ofparts of the screen<strong>in</strong>g woodlands, there is potential to <strong>in</strong>tegrate these <strong>in</strong>to a s<strong>in</strong>gle suite ofcontiguous habitat, physically cont<strong>in</strong>uous with Barnham Cross Common SSSI (also unfavourablerecover<strong>in</strong>g). Tak<strong>in</strong>g advantage of the hard barriers and lack of s<strong>in</strong>gle graz<strong>in</strong>g regime, areas ofungrazed physically disturbed habitat could be created as l<strong>in</strong>k<strong>in</strong>g elements along boundaries. Theneed to reta<strong>in</strong> screen<strong>in</strong>g for breed<strong>in</strong>g stone curlew will impose constra<strong>in</strong>ts on some boundaries, butit appears that current approaches to management of these sites are considered <strong>in</strong> isolation andwithout <strong>in</strong>tegration.193

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