Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm - Partnerships for Renewables Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm considered to materially contribute to a significant cumulative impact on the Westwater SPA, Ramsar Site and SSSI population or on the species at the NHZ level. 12.9 Summary of Effects 12.9.1 The baseline surveys conducted to inform the EIA have identified an ornithological assemblage within the vicinity of the development that is typical of plantation and upland habitats of Central/South-east Scotland, with usage within the application site boundary being confined mainly to relatively common breeding passerines and raptors. Although a number of species were identified as being of conservation concern, most were not considered significant within the context of their respective regional or national populations, and further consideration was not required within the EIA. This left three VORs to be taken into account in the impact assessment: goshawk, pink-footed goose and greylag goose. 12.9.2 The impact assessment identified that there would be no effects of habitat loss, disturbance, displacement or barrier effects on either pink-footed geese or greylag geese. Regarding collision mortality, although the proposed wind farm was predicted to result in the mortality of a small number of individuals from each of these species per year, the mortality rates were predicted to be well within acceptable levels when compared to regional population figures. 12.9.3 Importantly, survey data collected at both the proposed Camilty wind farm site and at the Westwater SPA, Ramsar site and SSSI (for which pink-footed goose is the qualifying feature) indicated that few of the pink-footed geese flying over Camilty were associated with the Westwater population. This, in conjunction with data from previous studies at Westwater, strongly suggests that there is little connectivity between the proposed Camilty wind farm site and the Westwater SPA for this qualifying feature. 12.9.4 With regard to goshawk, the impact assessment identified that the proposed wind farm would result in the potential loss of foraging and nesting habitat, disturbance and displacement of birds from suitable habitat associated with the general area of the proposed wind farm, and could potentially pose a barrier to the movement of locally occurring goshawks within their range. However, when considering the ongoing effects of forestry activities that the local goshawks have apparently adapted to, such effects were anticipated to have no more than slight adverse impacts on the regional goshawk population, which is considered to be not significant in terms of the EIA Regulations. With regard to collision mortality, the proposed wind farm was predicted to result in the collision of approximately one bird every three years. This predicted collision rate is thought to be precautionary and does not necessarily reflect the species typical below-canopy flight behaviour. However, when compared to background natural mortality figures this predicted collision rate was considered to have a level of effect of no more than slight on the regional goshawk population, and hence was not considered to be significant in terms of the EIA Regulations. 12.9.5 With regard to cumulative effects in combination with other wind farm developments it was concluded that any impacts on pink-footed geese or greylag geese would be of negligible level, whilst those on goshawk were of a slight level of effect. March 2013 12-66 ES Chapter 12 Ornithology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
Camilty Wind Farm Table 12.20 Summary of Level of Effects (and Significance) Receptor Sensitivity/ Importance of Receptor Effect Development Phase Magnitude of Change/Effect Level of Effect (and Significance) Prior to Mitigation Mitigation Enhancement Level of Effect (and Significance ) after Mitigation Nature of Effect Goshawk Regional Habitat loss (nesting) Construction Small (worst case scenario) Slight (not significant) Removal (felling) of nest site prior to construction and outside of the breeding season N/A Slight (not significant) Assumes theoretical loss of a nest site in the unlikely event that one is established within the development footprint Habitat loss (foraging) Construction Negligible Negligible (not significant) None N/A Negligible (not significant) None predicted Disturbance/ Displacement (nesting) Construction Small (worst case scenario) Slight (not significant) Pre- and midconstruction surveys to identify any goshawk nests and establishment of work exclusion zones where necessary N/A Slight (not significant) Assumes theoretical disturbance of a nest site in the unlikely event that one is established within the development footprint Disturbance/ Displacement (foraging) Construction Negligible Negligible (not significant) None N/A Negligible (not significant) Negligible displacement to alternative foraging areas March 2013 12-67 ES Chapter 12 Copyright Partnerships for Renewables Development Co. Ltd 2013 © Ornithology
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<strong>Camilty</strong> <strong>Wind</strong> <strong>Farm</strong><br />
considered to materially contribute to a significant cumulative impact on the Westwater SPA,<br />
Ramsar Site and SSSI population or on the species at the NHZ level.<br />
12.9 Summary of Effects<br />
12.9.1 The baseline surveys conducted to in<strong>for</strong>m the EIA have identified an ornithological<br />
assemblage within the vicinity of the development that is typical of plantation and upland<br />
habitats of Central/South-east Scotland, with usage within the application site boundary being<br />
confined mainly to relatively common breeding passerines and raptors. Although a number<br />
of species were identified as being of conservation concern, most were not considered<br />
significant within the context of their respective regional or national populations, and further<br />
consideration was not required within the EIA. This left three VORs to be taken into account<br />
in the impact assessment: goshawk, pink-footed goose and greylag goose.<br />
12.9.2 The impact assessment identified that there would be no effects of habitat loss, disturbance,<br />
displacement or barrier effects on either pink-footed geese or greylag geese. Regarding<br />
collision mortality, although the proposed wind farm was predicted to result in the mortality of<br />
a small number of individuals from each of these species per year, the mortality rates were<br />
predicted to be well within acceptable levels when compared to regional population figures.<br />
12.9.3 Importantly, survey data collected at both the proposed <strong>Camilty</strong> wind farm site and at the<br />
Westwater SPA, Ramsar site and SSSI (<strong>for</strong> which pink-footed goose is the qualifying feature)<br />
indicated that few of the pink-footed geese flying over <strong>Camilty</strong> were associated with the<br />
Westwater population. This, in conjunction with data from previous studies at Westwater,<br />
strongly suggests that there is little connectivity between the proposed <strong>Camilty</strong> wind farm site<br />
and the Westwater SPA <strong>for</strong> this qualifying feature.<br />
12.9.4 With regard to goshawk, the impact assessment identified that the proposed wind farm would<br />
result in the potential loss of <strong>for</strong>aging and nesting habitat, disturbance and displacement of<br />
birds from suitable habitat associated with the general area of the proposed wind farm, and<br />
could potentially pose a barrier to the movement of locally occurring goshawks within their<br />
range. However, when considering the ongoing effects of <strong>for</strong>estry activities that the local<br />
goshawks have apparently adapted to, such effects were anticipated to have no more than<br />
slight adverse impacts on the regional goshawk population, which is considered to be not<br />
significant in terms of the EIA Regulations. With regard to collision mortality, the proposed<br />
wind farm was predicted to result in the collision of approximately one bird every three years.<br />
This predicted collision rate is thought to be precautionary and does not necessarily reflect<br />
the species typical below-canopy flight behaviour. However, when compared to background<br />
natural mortality figures this predicted collision rate was considered to have a level of effect<br />
of no more than slight on the regional goshawk population, and hence was not considered to<br />
be significant in terms of the EIA Regulations.<br />
12.9.5 With regard to cumulative effects in combination with other wind farm developments it was<br />
concluded that any impacts on pink-footed geese or greylag geese would be of negligible<br />
level, whilst those on goshawk were of a slight level of effect.<br />
March 2013 12-66 ES Chapter 12<br />
Ornithology<br />
Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> Development Co. Ltd 2013 ©