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Scotland's Wildlife – an assessment of biodiversity in 20

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Six habitats assessed <strong>in</strong> the <strong>20</strong>05 report<strong>in</strong>g round were re-assessed <strong>in</strong> <strong>20</strong>08 (Table<br />

8.1): lowl<strong>an</strong>d mixed deciduous woodl<strong>an</strong>d; native p<strong>in</strong>e woodl<strong>an</strong>ds; upl<strong>an</strong>d mixed<br />

ashwoods; upl<strong>an</strong>d oakwood; wet woodl<strong>an</strong>d; <strong>an</strong>d wood-pasture & parkl<strong>an</strong>d.<br />

Assessments are based on systematic survey where possible, but sometimes rely on<br />

expert judgement.<br />

One <strong>of</strong> the habitats (wood-pasture & parkl<strong>an</strong>d) had been decl<strong>in</strong><strong>in</strong>g <strong>in</strong> <strong>20</strong>05 but by <strong>20</strong>08<br />

all were stable or <strong>in</strong>creas<strong>in</strong>g.<br />

Table 8.1<br />

Trends <strong>in</strong> woodl<strong>an</strong>d priority habitat status between <strong>20</strong>05 <strong>an</strong>d <strong>20</strong>08<br />

Source: Biodiversity Action Report<strong>in</strong>g System<br />

Woodl<strong>an</strong>d habitats <strong>20</strong>05 <strong>20</strong>08<br />

Assessed <strong>in</strong> both years count % count %<br />

Decl<strong>in</strong><strong>in</strong>g (slow<strong>in</strong>g) 1 17<br />

Fluctuat<strong>in</strong>g - probably decl<strong>in</strong><strong>in</strong>g<br />

No clear trend<br />

Fluctuat<strong>in</strong>g - probably stable 1 17<br />

Stable 1 17<br />

Fluctuat<strong>in</strong>g - probably <strong>in</strong>creas<strong>in</strong>g 1 17<br />

Increas<strong>in</strong>g 4 67 4 67<br />

The overall trend for woodl<strong>an</strong>d priority habitats is better.<br />

Priority species<br />

Some 170 <strong>biodiversity</strong> priority species (e.g. mosses, liverworts, fungi <strong>an</strong>d flower<strong>in</strong>g<br />

pl<strong>an</strong>ts; bees <strong>an</strong>d butterflies; mammals <strong>an</strong>d birds) occur <strong>in</strong> woodl<strong>an</strong>d ecosystems <strong>in</strong><br />

Scotl<strong>an</strong>d.<br />

Twenty-four species which were assessed <strong>in</strong> <strong>20</strong>05 were re-assessed <strong>in</strong> <strong>20</strong>08 (Table<br />

8.2): a lichen, Rothothelium dictyosporum; a lichen, Arthothelium macounii; a lichen,<br />

Bacidia <strong>in</strong>compta; a lichen, Biatoridium monasteriense; tree catapyrenium lichen,<br />

Catapyrenium psoromoides; a lichen, Pseudocyphellaria norvegica; a lichen,<br />

Schismatomma graphidioides; elm gyalecta lichen, Gyalecta ulmi; stump lichen,<br />

Cladonia botrytis; slender thread-moss, Orthodontium gracile; blunt-leaved bristle-moss,<br />

Orthotrichum obtusifolium; green shield moss, Buxbaumia viridis; tw<strong>in</strong>flower, L<strong>in</strong>naea<br />

borealis; juniper, Juniperus communis; narrow-headed <strong>an</strong>t, Formica exsecta; p<strong>in</strong>e<br />

hoverfly, Blera fallax; aspen hoverfly, Hammerschmidtia ferrug<strong>in</strong>ea; barred tooth-striped<br />

moth, Trichopteryx polycommata; dark-bordered beauty moth, Epione vespertaria;<br />

chequered skipper butterfly, Carterocephalus palaemon; red squirrel, Sciurus vulgaris;<br />

Europe<strong>an</strong> nightjar, Caprimulgus europaeus; Eurasi<strong>an</strong> wryneck, Jynx torquilla; western<br />

capercaillie, Tetrao urogallus.<br />

In <strong>20</strong>05, 30% were decl<strong>in</strong><strong>in</strong>g compared with 32% <strong>in</strong> <strong>20</strong>08. One species was thought to<br />

be no longer present <strong>in</strong> Scotl<strong>an</strong>d (Eurasi<strong>an</strong> Wryneck, Jynx torquilla). The proportion <strong>of</strong><br />

species that were stable or <strong>in</strong>creas<strong>in</strong>g rose from 41% <strong>in</strong> <strong>20</strong>05 to 49% <strong>in</strong> <strong>20</strong>08.<br />

54

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