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Forthbank Wind Energy Development - Partnerships for Renewables

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<strong>Forthbank</strong> <strong>Wind</strong> <strong>Energy</strong> <strong>Development</strong><br />

assessment of bat roost potential was undertaken following the guidelines published by<br />

English Nature 21 and the Bat Surveys Good Practice Guidelines 22 .<br />

11.2.35 The initial surveys carried out in April and early June, involving a dusk commuting watch and<br />

walked transects, revealed only low levels of bat activity at the site.<br />

11.2.36 Following the initial assessment, as noted in Table 11.1, SNH was consulted on and agreed to<br />

the bat survey aims, rationale and methodology described below.<br />

11.2.37 The survey aims were: to identify any high risk species present on site in the key periods<br />

during maternity and during mating/dispersal/migration; assess their activity level; locate roosts<br />

at significant risk of disturbance; and investigate the potential risk level of each species.<br />

11.2.38 The methodology <strong>for</strong> the surveys is adapted from the most recent Natural England and<br />

Eurobats guidelines 3,4 . Walked transect survey routes were designed based on the desktop<br />

study results and the initial site walkover to cover the habitats within the application area.<br />

Dawn and dusk surveys were used to monitor <strong>for</strong> commuting routes across the site and to<br />

indicate the presence of any significant nearby roosts. Control surveys were undertaken offsite<br />

during driven transect surveys to provide comparison of bat activity levels in some<br />

comparable nearby habitats, and these survey locations are shown in Figure 11.2. Passive<br />

monitoring using Anabat detectors was undertaken <strong>for</strong> periods of 2 weeks in the maternity<br />

season (between 15 and 28 July 2010) and again in the dispersal season (between 30 August<br />

and 15 September 2010), covering the development area.<br />

11.2.39 The survey routes and point count stops are marked on Figure 11.2. Point surveys of five<br />

minutes duration were undertaken along the route, at the proposed turbine locations and at<br />

representative areas of the habitats on site.<br />

11.2.40 Subsequent to the initial assessment visit in April, the site was visited on six separate<br />

occasions: 28 April, 01 June (delayed May visit), 24 June, 27 July, 29 August and a final visit<br />

on 20 September 2010. Transects were walked by experienced bat surveyors using Duet bat<br />

detectors and Zen MP3/WAV recording devices.<br />

11.2.41 Dusk commuting watches were undertaken at two vantage point locations (Figure 11.2) prior to<br />

the start of walked transects. The surveys started 30mins be<strong>for</strong>e sunset and had duration of<br />

1hour – 1.5hours depending on weather conditions.<br />

11.2.42 Driven transects and points, with the engine turned off to reduce disturbance, were undertaken<br />

on 1 June, 24 June, 29 August and 20 September 2010 during which bat passes were<br />

recorded by a bat surveyor out of the window of a slow driving car (15m/h) as recommended in<br />

the BCT Good Practice Guidelines 22 Error! Bookmark not defined., using a Duet bat detector<br />

and a Zen MP3/WAV recording device. The driven transect route is shown in Figure 11.2.<br />

11.2.43 Recordings from transects and dusk commuting watches were analysed with specialised<br />

software (BatSound, Wavesurfer, Analook) to determine/confirm bat species present.<br />

November 2010 Chapter 11 Page 8<br />

Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> <strong>Development</strong> Co. Ltd 2010 ©

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