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environmental statement - Rotherham's Online Application for ...

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experienced ecologists, holding a current Natural England whiteclawed<br />

crayfish survey licence. These watercourses are the northern<br />

and southern branches of Ulley Brook. The survey involved firstly a<br />

habitat assessment of the watercourse, recorded on a Crayfish Survey<br />

Form. The <strong>for</strong>ms provide background and habitat in<strong>for</strong>mation, including<br />

an assessment of channel substrate, potential <strong>for</strong> refuges and water<br />

quality. The position of any potential crayfish burrows were also<br />

marked, as well as any significant physical features which could be<br />

considered barriers to crayfish movement. The second part of the<br />

survey followed the standardised field survey methodology within the<br />

Survey and Monitoring Protocol <strong>for</strong> the White-Clawed Crayfish (Peay,<br />

2002). This was undertaken to determine presence/absence of whiteclawed<br />

crayfish. This entailed manual searching; carefully lifting and<br />

turning over suitable stones and debris on the channel bed and in the<br />

banks, which crayfish may use as refuge sites. Areas of habitat that<br />

appeared to be the most favourable <strong>for</strong> crayfish and could be physically<br />

searched were searched. These were searched in upstream direction<br />

to avoid poor visibility.<br />

Great Crested Newt (GCN) Survey: A single pond was identified<br />

adjacent to the southern boundary of the study area in June 2007, at<br />

which time it contained a shallow depth (3-4cm) of standing water and<br />

was completely overgrown with grass, rosebay willowherb (Chamerion<br />

angustifolium), bur-reed (Sparganium sp.), soft rush (Juncus effusus)<br />

and patches of watercress (Rorippa nasturtium-aquaticum). A Habitat<br />

Suitability Index survey (HSI) was undertaken in May 2008, according<br />

to HSI methodology produced by Oldham et al. (2000), which assumes<br />

that habitat quality determines GCN population size. The HSI provides<br />

a measure of habitat suitability and, whilst not being a substitute <strong>for</strong><br />

GCN surveys, is a useful tool in determining which ponds require GCN<br />

surveys. The HSI survey involved evaluating the pond against a<br />

number of key habitat criteria to derive a HSI index value between 0<br />

and 1, with 0 being highly unsuitable <strong>for</strong> great crested newt and 1 being<br />

an ideal pond <strong>for</strong> the species.<br />

Assessment of Significance<br />

7.12 The method of evaluation and assessment uses a combination of<br />

guidance from:<br />

Guidelines <strong>for</strong> Ecological Impact Assessment (Institute of Ecology and<br />

Environmental Management, 2006);<br />

Guidelines <strong>for</strong> Baseline Ecological Assessment (Institute of<br />

Environmental Assessment, 1995); and<br />

Handbook of Biodiversity Methods (RPS Group plc and Scottish<br />

Natural Heritage, 2005).<br />

172<br />

Penny Hill Wind Farm<br />

Environmental Statement

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