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Fen Management Handbook - Scottish Natural Heritage

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Examples of evaluation criteria for species<br />

Level of value Examples of qualifying Vertebrate Evaluation Criteria<br />

International Populations of regularly occurring globally threatened species (e.g. IUCN red listed species)<br />

Internationally important populations of a species (e.g. greater than 1% of a flyway population<br />

of birds)<br />

Nationally significant populations of an internationally important species<br />

Regularly occurring populations of internationally important species that are rare or threatened<br />

in the UK or of uncertain conservation status<br />

National Nationally important populations of a species (e.g. greater than 1% of the national population of<br />

a bird species)<br />

Significant populations of a nationally important species (e.g. UK Red Data Book species)<br />

UKBAP Priority Species requiring protection of all nationally important sites<br />

Regularly occurring populations of a nationally important species that is threatened or rare in<br />

the region or county<br />

Regional Regionally important populations of a species<br />

Significant populations of a regionally important species<br />

Regularly occurring, locally significant populations of species listed as nationally scarce (i.e.<br />

which occur in 16-100 10km squares in the UK), or Regional BAP species listed for regional<br />

rarity or localisation<br />

County /<br />

Metropolitan<br />

District /<br />

Borough<br />

Species populations of county importance (e.g. greater than 1% of the county population of a<br />

bird species)<br />

Significant populations of a county important species (e.g. species listed on a county BAP on<br />

account of rarity or localisation)<br />

Species populations of district importance<br />

Significant populations of a district / borough important species (e.g. species listed on a local<br />

BAP on account of rarity or localisation)<br />

For a site-based evaluation for management planning, the EcIA approach is a useful first step, but<br />

may not provide sufficient information on sites with low biodiversity value, or may give insufficient<br />

weight to site-specific factors. For example, if a site contains little biodiversity value, the EcIA<br />

approach may not offer sufficient distinction between features of low value. It may also undervalue<br />

populations of common or widespread species which have local significance for reasons other than<br />

rarity.<br />

In these instances, other considerations could be introduced into the evaluation process, such<br />

as flagship significance (e.g. a popular species that is valued by recreational users of the site) or<br />

historical significance (e.g. a population of a species known to have been present on the site for<br />

many years).<br />

The context of the site in the surrounding landscape should also be considered. For example, a site<br />

may contain small numbers of a nationally rare species, but larger numbers of a county rarity. It may<br />

be more appropriate to prioritise the county rarity over the national rarity if the national rarity is also<br />

found widespread on adjacent or nearby sites.<br />

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