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 there is an abundance of alternative and equally suitable goshawk foraging habitat in the wider Camilty area (at least 1500 ha within 3 km of the recent nest sites, as detailed above). In this context the loss of potential goshawk foraging habitat during construction would be very minor and therefore expected to have a negligible effect on the local goshawk population resulting in a Negligible level of effect, which would not be significant in terms of the EIA Regulations. Construction - Disturbance Nesting Habitat 12.5.31 It is feasible that construction works could cause disturbance to goshawk nesting in the currently used location, or elsewhere within, or near to, the proposed Camilty wind farm site should there be a future change in nesting site. 12.5.32 A survey of expert opinion identified that goshawks in Europe had a reasonably high level of tolerance to human disturbance and human-altered landscapes (Ruddock and Whitfield 2007). Evidence suggested that disturbance during the breeding season was found to elicit responses ranging from static (e.g. alarm calling) to active (e.g. taking flight) up to 750 m from a nest and that nest abandonment was likely to occur when the disturbance source was within 100 m of a nest site. Disturbance free zones of 400 m during the nest building and incubation period, reduced to 200 m once the young are at least 10 days old, have been advocated in several studies, although an upper disturbance free zone of 300-500 m is a more widely accepted precautionary range. 12.5.33 The currently used goshawk nest site lies beyond these distances of the proposed Camilty wind farm site. Furthermore, the previously used nest site in this area occurred within approximately 20 m of a forestry track which was used by dog walkers, motorcycles and forestry vehicles and was approximately 230 m from the A70 road (FHSE, 2012). Successful breeding occurred at this site, at least in 2011. Therefore, it is likely that birds occupying this territory are relatively tolerant of disturbance and less likely to be affected by construction activities. Consequently, if the existing nest site continues to be used, construction disturbance from the proposed development is expected to result in at most a small magnitude of effect on the population at both a local and regional scale. Combined with the medium conservation importance of this VOR, this would produce a Slight level of effect, which is not significant in terms of the EIA Regulations. 12.5.34 While other nest sites may be established within, or in close proximity to, the proposed development site between now and the commencement of construction of the proposed development, the likelihood of this is considered to be very low given the availability of suitable alternative nesting habitat in the wider Camilty area, as detailed above (see 12.5.27). Nonetheless, if a nest site were to be established in close proximity to the proposed development site then there would be potential for the nesting birds to be disturbed by the construction works. 12.5.35 In the event of a shift from the current nest site, the worst case scenario is that nesting occurs within 300 - 500m of construction-related activities on the proposed development site, which could result in the permanent loss of any eggs or young which had been produced and the short-term displacement to other locations in the surrounding area. Given the relatively small size of breeding goshawk population in south-east Scotland (28 pairs - Etheridge et al. 2012), the resulting breeding failure could be expected to have an effect of medium magnitude, leading to a Moderate level of effect. However, this is considered a highly unlikely March 2013 12-44 ES Chapter 12 Ornithology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©

Camilty Wind Farm scenario. Any change in nesting locations is more likely to result in nesting being at distances greater than 300 - 500m from construction-related activities on the proposed development site, so that the level of effect would be at most Slight (as for construction disturbance effects predicted at the currently used nest site – see 12.5.33). Foraging Habitat 12.5.36 As mentioned above, the vast majority of the proposed wind farm (over 90%) will be located within the clear-fell and recently restocked areas of the site. Although goshawks may still forage over and within these open areas there is considered to be an abundance of alternative and equally suitable goshawk foraging habitat in the wider Camilty area (at least 1500 ha within 3 km of the recent nest sites – see 12.5.27). Therefore, any birds which may be dissuaded from foraging over and within the proposed development site or the immediately surrounding area will simply be displaced to these other areas. Goshawks are also known to be relatively tolerant of human disturbance (Ruddock and Whitfield, 2007) and therefore foraging birds are unlikely to be significantly affected by ongoing construction works. Consequently, the effects of disturbance during construction are likely to be of negligible magnitude on the local goshawk population and therefore the level of effect is anticipated to be Negligible which is not significant in terms of the EIA Regulations. Operation - Disturbance/Displacement Nesting Habitat 12.5.37 As detailed above (12.5.33), the existing goshawk nest site is located sufficiently far from the proposed development site that disturbance from the proposed wind farm (either during construction or operation) is unlikely to affect nesting. Consequently, if the existing nest site continues to be used, operational disturbance from the proposed development is expected to result in at most a small magnitude of effect on the population at both a local and regional scale. Combined with the medium conservation importance of this VOR, this would produce a Slight level of effect, which is not significant in terms of the EIA Regulations 12.5.38 As argued above (12.5.34) it is unlikely that there will be a change in goshawk nest site that results in the establishment of a new site within 300 – 500m of the proposed turbine locations prior to the start of the operational phase. However, if this were to occur, then disturbance from the operational activities could (as a worst case scenario) lead to abandonment of the (theoretical) nest site, with an alternative site having to be established elsewhere within the 1500+ ha of potentially suitable nesting habitat in the wider Camilty area (and within 3km of the known recently occupied nest sites). 12.5.39 Given that this is what happened to the 2011 nest site as a result of the Phase 1 felling operations (and that the birds are nesting within a forest habitat in which there is a rotational felling cycle), it is anticipated that the local goshawks are relatively habituated to such displacement. Therefore, the worst case scenario effects are predicted to be of no more than small magnitude on VOR of medium conservation importance. In some circumstances, this displacement could result in a moderate to slight level of effect considering the regional importance of the goshawk population. However, the local goshawks have bred successfully in close proximity to felling operations (estimated to be in the region of 300-500 m) in both 2011 and 2012. It is therefore considered that any effects of disturbance and displacement on nesting goshawks will be no more than slight, which is not significant in terms of the EIA Regulations. March 2013 12-45 ES Chapter 12 Ornithology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©

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

scenario. Any change in nesting locations is more likely to result in nesting being at distances<br />

greater than 300 - 500m from construction-related activities on the proposed development<br />

site, so that the level of effect would be at most Slight (as <strong>for</strong> construction disturbance effects<br />

predicted at the currently used nest site – see 12.5.33).<br />

Foraging Habitat<br />

12.5.36 As mentioned above, the vast majority of the proposed wind farm (over 90%) will be located<br />

within the clear-fell and recently restocked areas of the site. Although goshawks may still<br />

<strong>for</strong>age over and within these open areas there is considered to be an abundance of<br />

alternative and equally suitable goshawk <strong>for</strong>aging habitat in the wider <strong>Camilty</strong> area (at least<br />

1500 ha within 3 km of the recent nest sites – see 12.5.27). There<strong>for</strong>e, any birds which may<br />

be dissuaded from <strong>for</strong>aging over and within the proposed development site or the<br />

immediately surrounding area will simply be displaced to these other areas. Goshawks are<br />

also known to be relatively tolerant of human disturbance (Ruddock and Whitfield, 2007) and<br />

there<strong>for</strong>e <strong>for</strong>aging birds are unlikely to be significantly affected by ongoing construction<br />

works. Consequently, the effects of disturbance during construction are likely to be of<br />

negligible magnitude on the local goshawk population and there<strong>for</strong>e the level of effect is<br />

anticipated to be Negligible which is not significant in terms of the EIA Regulations.<br />

Operation - Disturbance/Displacement<br />

Nesting Habitat<br />

12.5.37 As detailed above (12.5.33), the existing goshawk nest site is located sufficiently far from the<br />

proposed development site that disturbance from the proposed wind farm (either during<br />

construction or operation) is unlikely to affect nesting. Consequently, if the existing nest site<br />

continues to be used, operational disturbance from the proposed development is expected to<br />

result in at most a small magnitude of effect on the population at both a local and regional<br />

scale. Combined with the medium conservation importance of this VOR, this would produce a<br />

Slight level of effect, which is not significant in terms of the EIA Regulations<br />

12.5.38 As argued above (12.5.34) it is unlikely that there will be a change in goshawk nest site that<br />

results in the establishment of a new site within 300 – 500m of the proposed turbine locations<br />

prior to the start of the operational phase. However, if this were to occur, then disturbance<br />

from the operational activities could (as a worst case scenario) lead to abandonment of the<br />

(theoretical) nest site, with an alternative site having to be established elsewhere within the<br />

1500+ ha of potentially suitable nesting habitat in the wider <strong>Camilty</strong> area (and within 3km of<br />

the known recently occupied nest sites).<br />

12.5.39 Given that this is what happened to the 2011 nest site as a result of the Phase 1 felling<br />

operations (and that the birds are nesting within a <strong>for</strong>est habitat in which there is a rotational<br />

felling cycle), it is anticipated that the local goshawks are relatively habituated to such<br />

displacement. There<strong>for</strong>e, the worst case scenario effects are predicted to be of no more than<br />

small magnitude on VOR of medium conservation importance. In some circumstances, this<br />

displacement could result in a moderate to slight level of effect considering the regional<br />

importance of the goshawk population. However, the local goshawks have bred successfully<br />

in close proximity to felling operations (estimated to be in the region of 300-500 m) in both<br />

2011 and 2012. It is there<strong>for</strong>e considered that any effects of disturbance and displacement<br />

on nesting goshawks will be no more than slight, which is not significant in terms of the EIA<br />

Regulations.<br />

March 2013 12-45 ES Chapter 12<br />

Ornithology<br />

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

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