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the golden plover is not sufficient to reach the qualifying threshold for any form of national or international designation. 8.42 The recorded populations of sparrowhawk, kestrel, buzzard and lapwing do not fulfil the criteria for conservation value greater than Low (local). Golden plover is listed on Annex 1 of the EC Birds Directive and therefore the nature conservation value that has been assigned to this species is Medium (Regional/County); small numbers of this species were recorded fairly frequently at the site and this has been considered when assigning this nature conservation value. 8.43 Non-target species of conservation importance recorded regularly within the Ecological Survey Area include: yellowhammer, linnet, reed bunting, house sparrow (Passer domesticus), skylark, grey partridge, starling, song thrush (Turdus philomelos) and tree sparrow. These species are considered to be of Medium (Regional/County) value. 8.44 All other species recorded are considered to be of no more than Negligible (Parish) nature conservation value. CONSTRUCTION PHASE Disturbance 8.45 Disturbance during construction (including noise, vibration and light pollution from heavy machinery and human activity) has been assessed as a slight adverse impact for four non-target species (skylark, grey partridge, reed bunting and yellowhammer). There were no records of nesting raptors or other particularly sensitive groups (ducks and waders) within 500m of the proposed wind farm and application boundary. Therefore the impact magnitude for disturbance is neutral-minor negative for all remaining species, including target species and nonground nesting species of medium conservation concern, resulting in an impact significance of neutral-slight adverse for all other species during the construction phase. Habitat Loss 8.46 The wind farm will result in temporary loss of habitat during construction, which could have adverse effects on the availability of hunting/foraging, roosting and breeding territory for potentially all of the species recorded over the open habitats. However working areas and the site construction compound will be reinstated on completion of the wind farm, therefore habitat loss due to construction is anticipated to be a short term impact. The magnitude of impact for all birds recorded within this area is considered to be minor negative. The impact significance assessment for all species determined to be of national and regional conservation concern and all target species using the land within the application boundary is therefore slight adverse. This includes skylark, linnet, yellowhammer, 203 Penny Hill Wind Farm Environmental Statement
eed bunting, grey partridge, starling, song thrush, house sparrow, tree sparrow, golden plover and lapwing. 8.47 The impact significance assessment for all other species is considered to be neutral for habitat loss due to the impact magnitude being neutral, the conservation value of each species being low/negligible, or both of the above. OPERATIONAL PHASE Disturbance 8.48 Disturbance during operation (e.g. as a result of human activity and noise associated with maintenance visits), is expected to be considerably less than would occur during construction. Therefore the impact magnitude for disturbance is neutral-minor negative for all species, resulting in an impact significance of neutral-slight adverse for all other species. Displacement 8.49 The presence and operation of the turbines may cause visual, noise and vibration-related effects that could deter target species from using the site for foraging, hunting and breeding. The site is utilised by raptors and waders and these species groups are thought to be particularly sensitive to the effects of disturbance and barrier to movement. Low numbers of lapwing and golden plover were recorded foraging on arable land within the Ornithological Survey Area, however alternative habitat is readily available within the locality and region. Therefore it is anticipated that the magnitude of the potential impact on golden plover and lapwing will be minor negative. The impact significance scores for lapwing and golden plover are therefore slight adverse. 8.50 Alternative habitat for breeding and wintering raptors is readily available in the wider locality/region and therefore the effect of displacement is considered to be highly localised in this instance. The impact magnitude for displacement will therefore be minor negative for sparrowhawk, kestrel and buzzard. The impact significance values for sparrowhawk, kestrel and buzzard are therefore slight adverse. Collision Risk 8.51 Wind turbines can create a risk of birds colliding with moving turbine blades. The degree of risk depends on the biometrics of the species (e.g. size, flight speed etc.), flight behaviour, age/maturity of target birds, population size, habitat quality, weather conditions, wind turbine dimensions, layout and spacing. 8.52 Predicted collision mortalities for target species recorded within the Ornithological Survey Area are detailed in Table 11 of the ornithology report (Appendix 4) and these results indicate that the following mortality 204 Penny Hill Wind Farm Environmental Statement
Page 1 and 2:
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
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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 and 206: Very High (International); High (Na
Page 207: 8.34 Of the five species, one is in
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
Page 257 and 258: 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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