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Securing Biodiversity in Breckland - European Commission

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Losses of Characteristic LichensOf the assemblage of rare crustose lichens grow<strong>in</strong>g on compacted exposed chalk, two were restrictedto <strong>Breckland</strong> <strong>in</strong> the UK and a third was only recorded <strong>in</strong>land <strong>in</strong> the <strong>Breckland</strong>. These species havebeen subject to surveillance and survey over the last three decades and this shows that: the Starry Breck Lichen Buellia asterella is now ext<strong>in</strong>ct <strong>in</strong> the UK (post 1997). by 2002 the Scaly Breck Lichen Squamar<strong>in</strong>a lenitigera (restricted to <strong>Breckland</strong> with<strong>in</strong> the UK)had been lost from three of the four sites at which it still occurred <strong>in</strong> the 1980s and nowsurvives as only c.10 thalli at a s<strong>in</strong>gle site (B. Nichols pers. comm.). Scrambled-Egg Lichen Fulgensia fulgens with<strong>in</strong> the UK known <strong>in</strong>land at only a s<strong>in</strong>gle locality <strong>in</strong>the Wangford area of <strong>Breckland</strong> (where it had been recorded s<strong>in</strong>ce the late 1800s), wasextirpated <strong>in</strong> <strong>Breckland</strong> <strong>in</strong> 1993 or shortly after.<strong>Breckland</strong> colonies of these species occurred on areas of exposed chalk drift created between 1880-1945, by fl<strong>in</strong>t m<strong>in</strong><strong>in</strong>g, soil trench<strong>in</strong>g, track-ways, removal of material for road build<strong>in</strong>g and creation ofanti-glider trenches and mounds. There was a long delay before it was recognised that physicaldisturbance and creation of fresh bare chalk was essential for the rejuvenation and cont<strong>in</strong>ued vigourof colonies. Other factors <strong>in</strong>clud<strong>in</strong>g encroach<strong>in</strong>g trees, reduced w<strong>in</strong>d and drought exposure andpossible effect of aerial nitrogen deposition may also have contributed to decl<strong>in</strong>es and losses 2 . Turfstripp<strong>in</strong>g was eventually carried out at Lakenheath Warren <strong>in</strong> 1997 and a positive response ofSquamar<strong>in</strong>a lentigera and Buellia asterella was <strong>in</strong>itially noted. Turf stripp<strong>in</strong>g was also carried out atother key sites <strong>in</strong> the late 1990s (<strong>in</strong>clud<strong>in</strong>g Weet<strong>in</strong>g and Thetford Heaths). However, by this timeFulgensia fulgens had already been lost, despite attempts at translocation, Squamar<strong>in</strong>a lentigera wasrestricted to just two colonies and Buellia asterella to a s<strong>in</strong>gle locality, with surviv<strong>in</strong>g colonies of bothspecies already greatly reduced <strong>in</strong> extent. At Lakenheath Warren the last remnants of Buelliaasterella and Squamar<strong>in</strong>a lentigera were lost follow<strong>in</strong>g <strong>in</strong>troduction of cattle graz<strong>in</strong>g to the site <strong>in</strong>2000. Follow<strong>in</strong>g loss of the orig<strong>in</strong>al Squamar<strong>in</strong>a lentigera colony at Weet<strong>in</strong>g Heath <strong>in</strong> 1990/91(Gilbert 1991), a new colony of this species was discovered at this site by Bev Nichols <strong>in</strong> 1997, that<strong>in</strong>itially appeared to be stable <strong>in</strong> numbers, but this too now appears to be ext<strong>in</strong>ct, despite attemptsto create suitable new exposed chalk substrate.Recommendation: Surveillance and monitor<strong>in</strong>g of created chalk exposures should be repeated <strong>in</strong>termittently toexam<strong>in</strong>e whether rare terricolous lichen species re-colonise by long-distance spore transport.2 For a long time air pollution was blamed as caus<strong>in</strong>g simultaneous region-wide decl<strong>in</strong>es <strong>in</strong> these rare lichens andcerta<strong>in</strong>ly may have been a synergistic and contribut<strong>in</strong>g factor. However, <strong>in</strong> 1991 vigorous and thriv<strong>in</strong>g colonies ofSquamar<strong>in</strong>a lentigera occurred where bare compacted chalk was rejuvenated along a trackway, while abundant fruit<strong>in</strong>gof larger thalli was noted at rema<strong>in</strong><strong>in</strong>g colonies at decl<strong>in</strong><strong>in</strong>g sites <strong>in</strong> 1992 and 1997. Data held by Natural England showsthat, between 1973-1991, at Lakenheath Warren, most colonies were encroached by perennial grasses, Hieraciumpilosella, Cladonia rangiformis and creep<strong>in</strong>g mosses (particularly Hypnum cupressiforme). Crucially, the surface pH ofsubstrates was reduced, Watt (1940) recorded pH 7.9-8.2 for the top 4cm of Grassland A sites (Gilbert 1991; Hitch &Lambley 1993) <strong>in</strong> contrast on the Fulgensia mounds <strong>in</strong> 1991, values were substantially lower (pH 7.0-7.6 for soil 0-2cm or0-4cm).108

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