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b) Mapping of terrestrial habitat within 250 m of each pond to assess its suitability for great crested newts, covering a total area of 183.9 ha.

c) Collation of existing great crested newt count data from 1985 to 2005 for known display ponds within the SAC.

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b) Mapping of terrestrial habitat within 250 m of each pond to assess its suitability for great crested newts, covering a total area of 183.9 ha.

c) Collation of existing great crested newt count data from 1985 to 2005 for known display ponds within the SAC.

d) Condition assessment of great crested newts as a qualifying SAC feature.

This dataset forms part of the Wales-wide Common Standards Monitoring programme. The aim of the data collection was to assess the condition of designated SAC features against site-specific performance indicators, and to record aspects of their management to support management decisions and reporting at a range of spatial scales.</gmd:LocalisedCharacterString>
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                    <gmx:Anchor xlink:href="http://data.europa.eu/eli/reg/2010/1089">Commission Regulation (EU) No 1089/2010 of 23 November 2010 implementing Directive 2007/2/EC of the European Parliament and of the Council as regards interoperability of spatial data sets and services</gmx:Anchor>
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            <gco:CharacterString>A range of methodologies was employed during this survey.

Terrestrial habitat assessment

For the purposes of great crested newt monitoring, terrestrial habitat was defined by the Countryside Council for Wales as land within 250 m of each pond. Areas falling outside the SAC boundary were excluded from the assessment.

Maps showing a 250 m survey buffer around each pond were produced using MapInfo Professional v6.5 GIS software. A 10 m × 10 m grid was overlaid on the maps to enable terrestrial habitats to be classified at the required resolution.

Pond assessments

All 45 ponds were revisited on 23 August 2005 to undertake pond condition assessments. The following characteristics were estimated:

Percentage of the pond surface shaded by native macrophytes.
Percentage of the entire pond perimeter shaded to a distance of at least 1 m from the shoreline.
Percentage of the southern perimeter shaded.
Whether the pond was less than 10 cm deep at its deepest point.

Larval surveys

Torchlight surveys were undertaken on 23 August 2005 using a one-million candlepower Clulite torch at all ponds that still contained water. These surveys were carried out to determine the presence of great crested newt larvae and juveniles.

Egg searches

Natural and artificial egg-laying substrates within 1 m of the shoreline were inspected for the presence of Triturus cristatus eggs. At the same time, evidence of fish, waterfowl, invasive non-native species (such as Crassula helmsii), disturbance, or pollution was also recorded.</gco:CharacterString>
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                <gmd:LocalisedCharacterString locale="#EN">A range of methodologies was employed during this survey.

Terrestrial habitat assessment

For the purposes of great crested newt monitoring, terrestrial habitat was defined by the Countryside Council for Wales as land within 250 m of each pond. Areas falling outside the SAC boundary were excluded from the assessment.

Maps showing a 250 m survey buffer around each pond were produced using MapInfo Professional v6.5 GIS software. A 10 m × 10 m grid was overlaid on the maps to enable terrestrial habitats to be classified at the required resolution.

Pond assessments

All 45 ponds were revisited on 23 August 2005 to undertake pond condition assessments. The following characteristics were estimated:

Percentage of the pond surface shaded by native macrophytes.
Percentage of the entire pond perimeter shaded to a distance of at least 1 m from the shoreline.
Percentage of the southern perimeter shaded.
Whether the pond was less than 10 cm deep at its deepest point.

Larval surveys

Torchlight surveys were undertaken on 23 August 2005 using a one-million candlepower Clulite torch at all ponds that still contained water. These surveys were carried out to determine the presence of great crested newt larvae and juveniles.

Egg searches

Natural and artificial egg-laying substrates within 1 m of the shoreline were inspected for the presence of Triturus cristatus eggs. At the same time, evidence of fish, waterfowl, invasive non-native species (such as Crassula helmsii), disturbance, or pollution was also recorded.</gmd:LocalisedCharacterString>
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