Camilty Wind Farm - Partnerships for Renewables

Camilty Wind Farm - Partnerships for Renewables Camilty Wind Farm - Partnerships for Renewables

07.02.2014 Views

Camilty Wind Farm Bat Species 11.2.17 A series of field surveys were carried out to determine the presence of bat species, abundance, and the level of usage (flight activity) of the site by the bat species. The surveys carried out are listed below. A detailed description of the survey methodology and dates can be found in Appendix 11.3. Site Walkover 11.2.18 A daytime site walkover was undertaken on 19 February 2012 within the survey area (Figure 11.1 – Bat survey area within the blue-line boundary). The aim of this survey was to check and assess the potential value of habitats, features and structures present for roosting, foraging and commuting bats. Roost Surveys 11.2.19 All buildings identified within the bat survey area with the potential to support roosting bats were inspected externally by an experienced bat ecologist in good weather. This included seven structures that were all inspected on 2 July 2012, as shown on Figure 1 in Appendix 11.3. 11.2.20 The site predominantly contains coniferous plantation woodland with a mix of different age stands. The mature stands are predominantly Sitka spruce with a dense canopy and offer little potential for roosting bats. As no trees supporting, or with the potential to support roosting bats were identified, no further tree surveys were deemed necessary. Dusk Commuting Watch Surveys 11.2.21 Eight dusk commuting watches were undertaken between May and October 2012 (as indicated in Appendix 11.3) to assess the level of commuting activity to or across the site and to record early emerging, high risk species such as noctule bats (Nyctalus noctula). A single Vantage Point (as shown in Figure 1 in Appendix 11.3) was located on elevated ground near likely commuting routes in a habitat of greater suitability for bats. 11.2.22 The surveys started 30 minutes before sunset and had a duration of 1 hour – 1.5 hours depending on weather conditions; longer if the night was bright and might delay bat emergence. Surveyors recorded the flights of any bats observed commuting to/over the site. Walked Transect Survey 11.2.23 Eight walked transect surveys (Figure 11.6) were carried out between May and October 2012 in order to cover the following key activity periods for bats: • April-May (spring dispersal); • June-July (maternity season); • September-October (mating/dispersal season); and • October-November (dispersal season). 11.2.24 Transects were walked from 45 to 60 minutes after sunset for approximately 2 hours. Point surveys lasting 5 minutes were made along the route. This allowed for an assessment of bat commuting, foraging and roosting activity during the dispersal and mating seasons (Natural England, 2009). Routes and directions varied each month to ensure full coverage of the site and important habitats, and to minimise temporal bias in the results. March 2013 11-7 ES Chapter 11 Terrestrial Ecology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©

Camilty Wind Farm Driven Transect Survey 11.2.25 Driven transect surveys were undertaken following the walked transect or vantage points surveys between May and October, to gain an overview of bats using the site and wider area. 11.2.26 The transect routes (Figure 11.6) were driven with a maximum speed of not more than 15 mph, while an experienced bat surveyor held a Duet bat detector out of the open window to record any bat passes and species. Automated Anabat Passive Detector Surveys 11.2.27 Two remote recording bat detectors (Anabats) were positioned at two different locations on site during both the maternity and mating/dispersal periods to monitor bat activity (Table 11.2). Chosen locations reflected the habitat configuration within the survey area. A third Anabat was positioned at height (approximately at 65m) on the temporary met mast on site as Nathusius pipistrelle had been recorded in the area. Anabat detectors were programmed to record all bat activity starting at least one hour before sunset until at least one hour after sunrise. The location of the Anabat recording devices are shown in Figure 1 in Appendix 11.3. Table 11.2 Location and Recording of Deployed Anabats Anabat Grid reference Description Dates deployed Number of days 1 306277 659516 Open habitat, part clear-fell, part coniferous replant 25/05-12/06 2012 18 10/07-20/07/2012 10 13/08-03/09/2012 21 2 304851 658378 In forest plantation edge, near network of rides and open areas of coniferous replant 26/09-10/10/2012 14 25/05-12/06 2012 18 10/07-20/07/2012 10 13/08-03/09/2012 21 26/09-10/10/2012 14 Metmast 304900 659400 Installed at 65 m height on met mast May to October 2012 85 Great Crested Newt (Triturus cristatus) 11.2.28 The great crested newt Habitat Suitability Assessment (HSA) was undertaken by two RPS ecologists with experience of great crested newt ecology and HSAs on 28 September 2011. The assessment focussed on all ponds within 250 m of the Camilty site boundary. 11.2.29 Ponds were identified prior to going to site using aerial plans (e.g. the Google Maps 1 and Bing Maps 2 websites) and OS maps. The HSA was carried out using the Habitat Suitability 1 Google Maps (http://maps.google.co.uk). March 2013 11-8 ES Chapter 11 Terrestrial Ecology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©

<strong>Camilty</strong> <strong>Wind</strong> <strong>Farm</strong><br />

Bat Species<br />

11.2.17 A series of field surveys were carried out to determine the presence of bat species,<br />

abundance, and the level of usage (flight activity) of the site by the bat species. The surveys<br />

carried out are listed below. A detailed description of the survey methodology and dates can<br />

be found in Appendix 11.3.<br />

Site Walkover<br />

11.2.18 A daytime site walkover was undertaken on 19 February 2012 within the survey area (Figure<br />

11.1 – Bat survey area within the blue-line boundary). The aim of this survey was to check<br />

and assess the potential value of habitats, features and structures present <strong>for</strong> roosting,<br />

<strong>for</strong>aging and commuting bats.<br />

Roost Surveys<br />

11.2.19 All buildings identified within the bat survey area with the potential to support roosting bats<br />

were inspected externally by an experienced bat ecologist in good weather. This included<br />

seven structures that were all inspected on 2 July 2012, as shown on Figure 1 in Appendix<br />

11.3.<br />

11.2.20 The site predominantly contains coniferous plantation woodland with a mix of different age<br />

stands. The mature stands are predominantly Sitka spruce with a dense canopy and offer<br />

little potential <strong>for</strong> roosting bats. As no trees supporting, or with the potential to support<br />

roosting bats were identified, no further tree surveys were deemed necessary.<br />

Dusk Commuting Watch Surveys<br />

11.2.21 Eight dusk commuting watches were undertaken between May and October 2012 (as<br />

indicated in Appendix 11.3) to assess the level of commuting activity to or across the site and<br />

to record early emerging, high risk species such as noctule bats (Nyctalus noctula). A single<br />

Vantage Point (as shown in Figure 1 in Appendix 11.3) was located on elevated ground near<br />

likely commuting routes in a habitat of greater suitability <strong>for</strong> bats.<br />

11.2.22 The surveys started 30 minutes be<strong>for</strong>e sunset and had a duration of 1 hour – 1.5 hours<br />

depending on weather conditions; longer if the night was bright and might delay bat<br />

emergence. Surveyors recorded the flights of any bats observed commuting to/over the site.<br />

Walked Transect Survey<br />

11.2.23 Eight walked transect surveys (Figure 11.6) were carried out between May and October<br />

2012 in order to cover the following key activity periods <strong>for</strong> bats:<br />

• April-May (spring dispersal);<br />

• June-July (maternity season);<br />

• September-October (mating/dispersal season); and<br />

• October-November (dispersal season).<br />

11.2.24 Transects were walked from 45 to 60 minutes after sunset <strong>for</strong> approximately 2 hours. Point<br />

surveys lasting 5 minutes were made along the route. This allowed <strong>for</strong> an assessment of bat<br />

commuting, <strong>for</strong>aging and roosting activity during the dispersal and mating seasons (Natural<br />

England, 2009). Routes and directions varied each month to ensure full coverage of the site<br />

and important habitats, and to minimise temporal bias in the results.<br />

March 2013 11-7 ES Chapter 11<br />

Terrestrial Ecology<br />

Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> Development Co. Ltd 2013 ©

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!