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Fen Management Handbook - Scottish Natural Heritage

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Other than for rare or exceptional individual species, survey for particular species are generally less<br />

important than survey for overall interest and assemblages. Target species for detailed examination<br />

are likely to be determined by past records from a particular site, by identification of a habitat which<br />

appears particularly suitable for a rare species, and/or on the basis of the known fauna of nearby<br />

sites.<br />

Less frequent but more detailed survey is more effective for invertebrates than frequent superficial<br />

survey (though there may be exceptions if a single species is being monitored). One survey in each<br />

management planning period, undertaken in time to feed into the next management plan, is a good<br />

default frequency. However, limited survey funding on such occasions might well be better spent<br />

in answering specific questions arising from the first period of management rather than in more<br />

widespread monitoring or surveillance, provided the habitat response has been satisfactory.<br />

1.2 Evaluation<br />

Evaluation is the process of determining the value of the species assemblages and populations on<br />

a site. It enables the identification and prioritisation of the features of ecological interest present on<br />

site, and is therefore essential for setting objectives and targets for management and monitoring<br />

programmes.<br />

Evaluation should be considered alongside the data search and scoping survey process outlined<br />

above, as if funds are unavailable to carry out a comprehensive site audit, it may be necessary to<br />

allocate funds to surveys of particular species or groups based on an initial assessment of their likely<br />

presence and value (e.g. one would normally prioritise a survey of a UKBAP priority species over a<br />

species of less conservation concern).<br />

There are a variety of attributes of a species that may be used as criteria for selection. These can<br />

include legal protection status, appearance on conservation priority lists, identification as an interest<br />

feature of the site in its designation, population conservation status, commercial value (less likely to<br />

be appropriate for vertebrate and invertebrate species), rarity, endangerment (risk of extinction), role<br />

as a flagship/umbrella species, importance for ecosystem function (keystone species) and value as<br />

an indicator species. In practice, the first three of these attributes are the ones most likely to drive<br />

prioritisation for management planning.<br />

The main factors used to determine value are<br />

– conservation priority (i.e. species which are rare or declining)<br />

– abundance (presence of a significant numbers or proportion of a population, regardless of<br />

conservation status) [e.g. 1% criteria for birds]<br />

For ecological impact assessment, species are often assigned a value on a scale ranging from<br />

international/national (e.g. a nationally significant population of a nationally rare species) through<br />

to local (e.g. a population of a species significant at the local level only). An example of this type of<br />

scale is provided in the table below, adapted from Hill et al (2005).<br />

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