Scotland's Wildlife â an assessment of biodiversity in 20
Scotland's Wildlife â an assessment of biodiversity in 20
Scotland's Wildlife â an assessment of biodiversity in 20
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Four habitats assessed <strong>in</strong> <strong>20</strong>05 were re-assessed <strong>in</strong> <strong>20</strong>08 (Table 9.1): bl<strong>an</strong>ket bog;<br />
limestone pavement; upl<strong>an</strong>d calcareous grassl<strong>an</strong>d; upl<strong>an</strong>d heathl<strong>an</strong>d. Assessments are<br />
based on systematic survey where possible, but sometimes rely on expert judgement.<br />
All four habitats were <strong>in</strong> decl<strong>in</strong>e (slow<strong>in</strong>g) <strong>in</strong> <strong>20</strong>05, but one had become stable by <strong>20</strong>08<br />
(limestone pavement).<br />
Table 9.1<br />
Trends <strong>in</strong> upl<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 />
Upl<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) 4 100 3 75<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<br />
Stable 1 25<br />
Fluctuat<strong>in</strong>g - probably <strong>in</strong>creas<strong>in</strong>g<br />
Increas<strong>in</strong>g<br />
The overall appraisal <strong>of</strong> upl<strong>an</strong>d priority habitats is better.<br />
Priority species<br />
Some 122 <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> Scottish upl<strong>an</strong>d ecosystems.<br />
Thirteen species which were assessed <strong>in</strong> <strong>20</strong>05 were re-assessed <strong>in</strong> <strong>20</strong>08 (Table 9.2): a<br />
lichen, Alectoria ochroleuca; northern prongwort (liverwort), Herbertus borealis; leadmoss,<br />
Ditrichum plumbicola; stalked puffball, Tulostoma niveum; Norwegi<strong>an</strong> mugwort<br />
(flower<strong>in</strong>g pl<strong>an</strong>t), Artemisia norvegica; Shetl<strong>an</strong>d mouse-ear (flower<strong>in</strong>g pl<strong>an</strong>t), Cerastium<br />
nigrescens; sword grass, Xylena exsoleta; mounta<strong>in</strong> scurvy-grass, Cochlearia micacea;<br />
yellow marsh saxifrage, Saxifraga hirculus; oblong woodsia, Woodsia ilvensis; wooly<br />
willow, Salix l<strong>an</strong>ata; argent <strong>an</strong>d sable moth, Rheumaptera hastate; <strong>an</strong>d netted mounta<strong>in</strong><br />
moth, Macaria carbonaria.<br />
In <strong>20</strong>05 <strong>an</strong>d <strong>20</strong>08, 8% were decl<strong>in</strong><strong>in</strong>g (the decl<strong>in</strong><strong>in</strong>g status <strong>of</strong> flower<strong>in</strong>g pl<strong>an</strong>t Shetl<strong>an</strong>d<br />
Mouse-ear, Cerastium nigrescens deteriorated). The number <strong>of</strong> species which were<br />
stable or <strong>in</strong>creas<strong>in</strong>g (84%) also rema<strong>in</strong>ed the same (although wooly willow, Salix l<strong>an</strong>ata,<br />
ch<strong>an</strong>ged from <strong>in</strong>creas<strong>in</strong>g to stable).<br />
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