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(approximately 2km to the west of the proposed wind farm site) and Brampton Park (to the east). In winter, Ulley Reservoir Country Park supports locally important populations of dabbling and diving ducks (teal Anas crecca, mallard A. platyrhynchos, wigeon A. penelope, gadwall A. strepera, tufted duck Aythya fuligula and pochard Aythya farina). Flocks of golden plover (Pluvialis apricaria) and pink-footed goose (Anser brachyrhynchus) have also been recorded over-flying the site. There are several records of peregrine (Falco peregrinus) and a single record of merlin (Falco columbarius) and hen harrier (Circus cyaneus) during the non breeding season. The park also supports a small breeding population of waterfowl. 8.28 At Brampton Park, there are historic records of breeding redshank, snipe and lapwing. Other breeding bird species include corn bunting (Miliaria calandra) and tree sparrow (Passer montanus), both of which are BoCC Red List and UK BAP species). Both Ulley Country Park and Brampton Park qualify as Candidate Local Wildlife Sites and Natural History Heritage Sites according to site designations adopted by Rotherham MBC. 8.29 Rother Valley Country Park (approximately 5km to the south) supports large populations of wintering waterfowl (including wildfowl and waders) and a wide range of nationally scarce passage migrant species have been recorded over an extended period of time, usually in small numbers. Breeding Bird Survey 8.30 A total of 41 species were recorded over the course of the three visits to the Ornithological Survey Area, of which 40 of these species were considered to be breeding within this area. There was a large degree of consistency between the four visits in terms of the bird species recorded and their numbers and locations. Full details of the results are included in the report in Appendix 4. 8.31 No species listed on Annex 1 of the Habitats Directive or Schedule 1 of the Wildlife and Countryside Act 1981 (as amended) were recorded. A number of species of high conservation concern that appear on the BoCC Red List were recorded during the survey visits. Breeding populations of eight BoCC Red List species were recorded within the Ornithological Survey Area. 8.32 Six species of medium conservation concern that appear on the BoCC Amber List were also recorded during the survey visits. Wintering Vantage Point Survey 8.33 A total of 33 non-target and 5 target (golden plover, kestrel, lapwing, buzzard and sparrowhawk) bird species were recorded over the course of the wintering bird vantage point survey. 201 Penny Hill Wind Farm Environmental Statement
8.34 Of the five species, one is included in Annex 1 of the EC Birds Directive 1979 (79/409/EEC) (golden plover) and three appear on the BoCC Amber List (kestrel Falco tinnunculus, lapwing Vanellus vanellus and golden plover). Lapwing is also listed on one or more of the UK Habitat Action Plans. Two of the target bird species are not included within any of the three conservation and legislation status indicators mentioned above (buzzard Buteo buteo and sparrowhawk Accipiter nisus). 8.35 A number of the non-target species recorded are included on the BoCC Red List. These included large flocks of Linnet (Carduelis cannabinat), which were frequently recorded, two reed bunting (Emberiza schoeniclus), small groups of yellowhammer (E. citrinella), skylark (Alauda arvensis), starling (Sturnus vulgaris) and grey partridge (Perdix perdix). 8.36 Common passerines were recorded such as: blackbird (Turdus merula), chaffinch (Fringilla coelebs), carrion crow (Corvus corone), blue tit (Cyanistes caeruleus), dunnock (Prunella modularis, [BoCC Amber List], goldfinch (Carduelis carduelis, great spotted woodpecker (Dendropcopos major), great tit (Parus major), greenfinch (Carduelis chloris), jackdaw (Corvus monedula), jay (Garrulus glandarius), magpie (Pica pica), meadow pipit (Anthus pratensis [BoCC Amber List]), mistle thrush (Turdus viscivorus [BoCC Amber List]), pied wagtail (Motacilla alba), redwing (Turdus iliacus [BoCC Amber List]), robin (Erithacus rubecula), starling (BoCC Red List), stock dove (Columba oenas [BoCC Amber List]), wood pigeon (Columba palumbus) and wren (Troglodytes troglodytes). 8.37 Flocks of fieldfare (Turdus pilaris) were also recorded. This species is included in Schedule 1 of the Wildlife and Countryside Act 1981 (as amended). 8.38 Other birds recorded include individuals and flocks of black headed gull (Larus ridibundus [BoCC Amber List]), common gull (Larus canus), grey partridge (BoCC Red List), herring gull (Larus argentatus [BoCC Amber List]), lesser black-backed gull (Larus fuscus [BoCC Amber List]), pheasant (Phasianus colchicus) and red legged partridge (Alectoris rufa). 8.39 None of the non-target species are included in Annex 1 of EC Birds Directive 1979 (79/409/EEC). ASSESSMENT OF EFFECTS 8.40 There are no statutory designated areas of natural heritage interest within the Study Area. There are two non-statutory sites within the Study Area, both of which are registered as Natural History Heritage Sites and Candidate Local Wildlife Site: Ulley Country Park and Brampton Common. Neither of these sites is likely to be affected either directly or indirectly by the construction and operation of the proposed wind farm. 8.41 The vantage point surveys recorded one species listed in Annex 1 of the EC Birds Directive (golden plover). However, the recorded population of 202 Penny Hill Wind Farm Environmental Statement
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PENNY HILL WIND FARM ENVIRONMENTAL
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PREFACE This Environmental Statemen
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TABLE OF CONTENTS PREFACE .........
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1. INTRODUCTION THIS DOCUMENT 1.1 T
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a summary of the assessment, includ
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to ensure that every home is adequa
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PROJECT OBJECTIVES 1.27 The project
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and enhanced wildlife habitats. In
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2.6 The proposed turbines would be
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Meteorological Monitoring 2.17 Wind
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2.26 Tracks between turbines are re
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include an appropriate control mech
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3. ENVIRONMENTAL IMPACT ASSESSMENT
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SCOPING AND CONSULTATION Submission
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elevant to each assessment are incl
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Impact on Landscape Impact on TV Re
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Regulations, it is important that t
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4. SITE SELECTION AND DESIGN DESCRI
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45m AGL as viable (using the BERR U
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4.26 Again there are no scheduled a
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environmental sieves must be consid
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Achieve acceptable noise levels fro
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5. CONSTRUCTION, OPERATION AND DECO
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Reinstatement around turbines; Cons
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5.21 If necessary, to prevent mud e
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turbine would automatically be appl
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PART 2: SUMMARY OF ENVIRONMENTAL IM
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ASSESSMENT METHODOLOGY Published Gu
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6.15 It is acknowledged that beyond
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6.30 The viewpoints were selected t
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6.42 The assessment records no effe
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Table 6.3: Photomontages A photomon
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6.51 With regards to the landscape
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No Change No notable loss or altera
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IMPACT SIGNIFICANCE 6.70 The ultima
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designated are clearly outweighed b
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6.91 ENV2.2 Interest Outside Statut
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PLANNING DESIGNATIONS 6.99 All rele
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6.115 In the wider 20km study area
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BASELINE CONDITIONS Site Specific L
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oundaries are marked by hedges. On
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Landscape Character Areas (LCAs) ar
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Countryside Commission and English
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Table 6.5: Sensitivity of Surroundi
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Laughton Common; Todwick Grange; To
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6.178 The Rotherham Roundwalk passe
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6.195 Tables 6.6 identifies the vie
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ASSESSMENT OF EFFECTS EFFECTS ON EX
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Operational Phase 6.219 As discusse
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The distance between the character
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distance, the turbines would be bar
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6.256 Therefore, it is considered t
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Nature and Magnitude of Constructio
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6.283 It should be noted that a num
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Decommissioning Phase 6.299 The onl
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6.317 Where there are clear views o
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6.334 From properties on the easter
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6.350 Therefore there would be a lo
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6.365 Therefore there would be no a
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Decommissioning Phase 6.381 The onl
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of the M18, the turbines would resu
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6.413 The top of the meteorological
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such the only properties within the
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would also be visible but at this d
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Significance of Construction Effect
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Nature and Magnitude of Operational
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6.507 The view towards the site fro
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number of locations along the publi
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6.557 The photograph presented in F
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Significance of Construction Effect
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6.591 The ZTV and wireframe suggest
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6.609 The development would result
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Reference Number Viewpoint Location
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There is no view from ground floor
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6.630 Beyond 5km any views of the P
Page 155 and 156: motorway. As the M1 approaches the
Page 157 and 158: 6.658 Therefore there would be a mo
Page 159 and 160: 6.671 The overall magnitude of chan
Page 161 and 162: 6.682 From these isolated locations
Page 163 and 164: Table 6.9: Summary of Theoretical S
Page 165 and 166: 6.697 An iterative design approach
Page 167 and 168: there is already considerable movem
Page 169 and 170: 6.724 It is the professional opinio
Page 171 and 172: 6.739 It has also been assessed tha
Page 173 and 174: Planning Policy Statement (PPS) 9:
Page 175 and 176: Phase 1 Habitat Survey; Bat Surveys
Page 177 and 178: experienced ecologists, holding a c
Page 179 and 180: 7.17 Residual effects of large adve
Page 181 and 182: 7.30 Two transects were surveyed wh
Page 183 and 184: No water was visible until the vege
Page 185 and 186: area is not considered to be a popu
Page 187 and 188: considered to be minor negative - t
Page 189 and 190: likelihood of this occurrence the i
Page 191 and 192: Bats 7.70 It is likely that there w
Page 193 and 194: 7.83 Where hedgerow sections are re
Page 195 and 196: there are plans for light work such
Page 197 and 198: Impact (Construction) Soil and wate
Page 199 and 200: Impact (Decommissioning) Ecological
Page 201 and 202: 8. ORNITHOLOGY INTRODUCTION 8.1 Thi
Page 203 and 204: Sheffield City Ecology Unit; Sheffi
Page 205: Very High (International); High (Na
Page 209 and 210: eed bunting, grey partridge, starli
Page 211 and 212: eeding season so that site compound
Page 213 and 214: Potential Effect Significance witho
Page 215 and 216: 9.7 For night time periods the reco
Page 217 and 218: industrial noise exceeds those abou
Page 219 and 220: Receptor Easting (m) Northing (m) E
Page 221 and 222: Morthen (H1) Brampton-en-le-morthen
Page 223 and 224: Morthen (H1) Brampton-en-lemorthen
Page 225 and 226: 9.37 The manufacturer of the turbin
Page 227 and 228: Cumulative Effects - consideration
Page 229 and 230: Visual Assessment of Wind Farms - B
Page 231 and 232: farm may be viewed, whether the tur
Page 233 and 234: given to either the nearest turbine
Page 235 and 236: from the proposed development (whic
Page 237 and 238: Table 10.6 - Grade I and II* Listed
Page 239 and 240: will add another layer to the recor
Page 241 and 242: SCHEDULE ANCIENT MONUMENTS 10.63 Th
Page 243 and 244: of the proposed development to the
Page 245 and 246: considered to be “negligible” i
Page 247 and 248: neighbouring properties of the sett
Page 249 and 250: not being considered significant fo
Page 251 and 252: CUMULATIVE IMPACT ASSESSMENT 10.110
Page 253 and 254: PART 3: DESCRIPTION OF OTHER EFFECT
Page 255 and 256: „The Environmental Statement shou
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oth lanes on the eastern approach t
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A631 Bawtry Road, Hellaby - 25,442
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PROPOSED TRANSPORT DATA Proposed Tr
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11.38 Based on the traffic levels i
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Table 11.4: Peak Increases in Traff
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Extended Servicing - One visit per
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Route 5 - M1 Junction 33 to M1 Junc
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Figure 11.2: The Penny Hill Site an
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High Volts Wind Farm, Hartlepool 11
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MITIGATION however, likely to be lo
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The strategic road network will be
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11.104 It is not considered that vi
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Figure 12.1: Penny Hill Site and Ci
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GAMSTON 12.17 Gamston is a licensed
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SUMMARY OF EFFECTS 12.34 It has bee
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13.6 The FRA has been based on a de
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13.21 A Coal Authority Mining Repor
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FLOODING FROM SURFACE WATER DRAINAG
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equired, there is no requirement to
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links, 3 T-Mobile links, 5 Vodafone
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Mll Telecom Ltd - Responded stating
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15. SHADOW FLICKER INTRODUCTION 15.
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PREDICTED EFFECTS 15.10 Table 15.1
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„health effects arising from shad
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16. OTHER ISSUES INTRODUCTION 16.1
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deliver effective environmental man
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falling from the blades and therefo
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Similarly, there is no statutory se
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All fields containing turbines woul
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