Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm - Partnerships for Renewables Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm Table 12.13 Species of Conservation Value Recorded During the Breeding Season Point Count Surveys Species Status Peak surve y count Relati ve abund ance* Annex I Sched ule 1 BoCC Redlisted BoCC Amber -listed SBL West Lothian LBAP Bullfinch Breeding 1 (Apr) 12% Crossbill sp. Breeding 8 (Apr) 47% Curlew Breeding 2 (May) Dunnock Breeding 7 (May) 12% 53% Linnet Flying over 1 (Jun) 6% Lesser redpoll Breeding 13 (Apr) 53% Mistle thrush Breeding 1 (Apr) 12% Meadow pipit Breeding 18 (Jun) 41% Siskin Breeding 21 (Apr) 76% Starling Flying over 4 (Jun) 6% Swallow Flying over 10 (Jun) 12% Song thrush Breeding 17 (Jun) 82% Whitethroat Breeding 1 (Apr) 12% Willow warbler Breeding 20 (Jun) 76% * the index of relative abundance represents the percentage of points at which each species was recorded across the three survey visits Winter Season Point Count Surveys 12.3.22 A total of 30 species were recorded during the winter season point count surveys (see Table 12.A.13 Appendix 12.1) of which only 10 were target species. These species are listed in Table 12.14. No Annex 1 species were recorded although the Schedule 1 species crossbill, fieldfare and redwing were present. Fieldfare and redwing were also the only red-listed species recorded, whilst there were also seven amber-listed species (bullfinch, dunnock, greylag goose, kestrel, mallard, pink-footed goose and woodcock) recorded. Of these, several species are also represented on the Scottish Biodiversity List. March 2013 12-22 ES Chapter 12 Ornithology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
Camilty Wind Farm Table 12.14 Winter Season Point Count Survey Results for Camilty Species Peak survey count Relative abundanc e* Annex I Schedule 1 BoCC Redlisted BoCC Amber -listed SBL West Lothian LBAP Bullfinch 4 (Nov) 25% Crossbill sp. 32 (Jan) 75% Dunnock 4 (Nov) 31% Fieldfare 40 (Nov) 6% Greylag goose 1 (Jan) 6% Kestrel 2 (Nov) 19% Mallard 4 (Nov) 6% Pink-footedgoose 37 (Nov) 6% Redwing 30 (Nov) 6% Woodcock 2 (Nov) 13% * the index of relative abundance represents the percentage of points at which each species was recorded across the three survey visits Pink-footed Goose Connectivity and Roost Surveys 12.3.23 Large numbers of pink-footed geese were recorded at the Westwater roost site between late September and late November 2012, with counts peaking at over 20,000 birds (Table 12.A.15, Appendix 12.1). During the Westwater surveys relatively few of the pink-footed geese using this roost departed in the direction of Camilty when leaving the site at dawn, or arrived back to the site from the direction of Camilty at dusk. Thus, an average of 3.3% of all dawn departures and dusk arrivals were considered to be on flight-lines that were in the direction of Camilty (as determined by the proportion of birds recorded within the 45 o arc directed towards Camilty), with this value never exceeding 16% on any survey (Table 12.A.15, Appendix 12.1). 12.3.24 Numbers of pink-footed geese recorded during the simultaneous surveys at the proposed Camilty wind farm site ranged from 0 to c.1200-1300. A variable, but sometimes high, proportion of these birds were recorded flying in a direction that was closely aligned with the direction to Westwater, but overall the counts during these surveys at Camilty represented a small proportion of the counts of departing or returning birds at Westwater, with this being less than 3% in five of the seven surveys from which these data could be extracted (Table 12.A.16, Appendix 12.1). In one other survey, the Camilty count represented c.18% of the coincident count at Westwater, whilst in the remaining instance it exceeded the Westwater count, occurring as it did in late November, when numbers at Westwater had declined to low levels (see Appendix 12.1 for details). 12.3.25 No pink-footed geese were recorded on, or flying onto, Cobbinshaw Reservoir during any of the eight dusk surveys carried out at this reservoir. March 2013 12-23 ES Chapter 12 Ornithology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
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<strong>Camilty</strong> <strong>Wind</strong> <strong>Farm</strong><br />
Table 12.14 Winter Season Point Count Survey Results <strong>for</strong> <strong>Camilty</strong><br />
Species<br />
Peak<br />
survey<br />
count<br />
Relative<br />
abundanc<br />
e*<br />
Annex<br />
I<br />
Schedule<br />
1<br />
BoCC<br />
Redlisted<br />
BoCC<br />
Amber<br />
-listed<br />
SBL<br />
West<br />
Lothian<br />
LBAP<br />
Bullfinch 4 (Nov) 25% <br />
Crossbill sp. 32 (Jan) 75% <br />
Dunnock 4 (Nov) 31% <br />
Fieldfare 40 (Nov) 6% <br />
Greylag goose 1 (Jan) 6% <br />
Kestrel 2 (Nov) 19% <br />
Mallard 4 (Nov) 6% <br />
Pink-footedgoose<br />
37 (Nov) 6% <br />
Redwing 30 (Nov) 6% <br />
Woodcock 2 (Nov) 13% <br />
* the index of relative abundance represents the percentage of points at which each species was recorded across the<br />
three survey visits<br />
Pink-footed Goose Connectivity and Roost Surveys<br />
12.3.23 Large numbers of pink-footed geese were recorded at the Westwater roost site between late<br />
September and late November 2012, with counts peaking at over 20,000 birds (Table<br />
12.A.15, Appendix 12.1). During the Westwater surveys relatively few of the pink-footed<br />
geese using this roost departed in the direction of <strong>Camilty</strong> when leaving the site at dawn, or<br />
arrived back to the site from the direction of <strong>Camilty</strong> at dusk. Thus, an average of 3.3% of all<br />
dawn departures and dusk arrivals were considered to be on flight-lines that were in the<br />
direction of <strong>Camilty</strong> (as determined by the proportion of birds recorded within the 45 o arc<br />
directed towards <strong>Camilty</strong>), with this value never exceeding 16% on any survey (Table<br />
12.A.15, Appendix 12.1).<br />
12.3.24 Numbers of pink-footed geese recorded during the simultaneous surveys at the proposed<br />
<strong>Camilty</strong> wind farm site ranged from 0 to c.1200-1300. A variable, but sometimes high,<br />
proportion of these birds were recorded flying in a direction that was closely aligned with the<br />
direction to Westwater, but overall the counts during these surveys at <strong>Camilty</strong> represented a<br />
small proportion of the counts of departing or returning birds at Westwater, with this being<br />
less than 3% in five of the seven surveys from which these data could be extracted (Table<br />
12.A.16, Appendix 12.1). In one other survey, the <strong>Camilty</strong> count represented c.18% of the<br />
coincident count at Westwater, whilst in the remaining instance it exceeded the Westwater<br />
count, occurring as it did in late November, when numbers at Westwater had declined to low<br />
levels (see Appendix 12.1 <strong>for</strong> details).<br />
12.3.25 No pink-footed geese were recorded on, or flying onto, Cobbinshaw Reservoir during any of<br />
the eight dusk surveys carried out at this reservoir.<br />
March 2013 12-23 ES Chapter 12<br />
Ornithology<br />
Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> Development Co. Ltd 2013 ©