B6N'%%. KDAJB:* 9D8JB:CI+ EGD?:8I 6EE:C9>8:H ^^
F?D;MEE: :CK>GDCB:CI6AHI6I:B:CIKDAJB:*/
Pinewood Studios Ltd Pinewood ES Volume 5 Appendices (ii)
Contents Appendix 10.1 Main Site Extended Phase1 Habitat Survey Report Appendix 10.2 Main Site Bat Survey Report Appendix 10.3 Main Site Great Crested Newt Survey Report Appendix 10.4 Main Site Dormouse and Badger Survey Report Appendix 10.5 Main Site Reptile Survey Report Appendix 10.6 Main Site Breeding Bird Survey Report Appendix 10.7 Main Site Wintering Bird Survey Report Appendix 10.8 Main Site Invertebrate Survey Report Appendix 10.9 Main Site Botanical Survey Species List Appendix 10.10 Main Site Tree Appraisal Appendix 10.11 Highways Infrastructure Extended Phase 1 Survey Report Appendix 10.12 Highways Infrastructure Protected Species Survey Report Appendix 10.13 Ecology Strategy Appendix 11.1 Extracts from Envirocheck Report Appendix 11.2 Stabilisation Date Criteria - Extract from Section 106 Agreement Appendix 11.3 Logs of Boreholes and Trial Pits, Concept 2008 Appendix 11.4 Screening of Soil Chemical Testing Results, Concept 2008 Appendix 11.5 Screening of Groundwater and Surface Water Chemical Testing Results, Concept 2008 Appendix 11.6 Data obtained from BCC : Landfill Gas Concentrations, Leachate Quality Analyses, Leachate Level and Groundwater Level Measurements Appendix 11.7 Screening of Landfill Leachate Chemical Testing Results, Concept 2008 Appendix 11.8 Ground Gas Monitoring Data, Concept 2008 Appendix 12.1 Infrastructure Drawings Appendix 12.2 EA Scoping Opinion Appendix 12.3 Flood Risk Assessment Appendix 13.1 Construction Waste Forecasts for the Proposed Development Appendix 13.2 Construction Waste Forecast for the Pinewood Studios Masterplan Appendix 13.3 Operational Waste Forecast for the Proposed Development
J:\207000\207042 PINEWOOD STUDIOS\14 EIA\ES\ES + APPENDICES ISSUE FINAL\APPENDICES\SS\COMPLETE APPENDICES SS\HEADER PAGE VOL 5.DOC Ove Arup & Partners Ltd Issue May 2009 Pinewood Studios Ltd Pinewood ES Volume 5 Appendices (ii)
J:\207000\207042 PINEWOOD STUDIOS\14 EIA\ES\ES + APPENDICES ISSUE FINAL\APPENDICES\SS\COMPLETE APPENDICES SS\HEADER PAGE VOL 5.DOC S2-1 Ove Arup & Partners Ltd Issue May 2009
______ecosulis ltd _
DTZCON-PINSTU-1480
EXTENDED PHASE 1 HABITAT SURVEY AND WINTER BIRD SCOPING
SURVEY OF LAND AT PINEWOOD STUDIOS, IVER HEATH,
BUCKINGHAMSHIRE
EXECUTIVE SUMMARY
EXTENDED PHASE 1 HABITAT SURVEY AND WINTER BIRD SCOPING In February 2008, ecosulis ltd was commissioned by DTZ Consulting and Research to SURVEY OF LAND AT PINEWOOD STUDIOS, IVER HEATH, undertake an extended Phase 1 habitat survey and wintering bird scoping survey of land at BUCKINGHAMSHIRE Pinewood Studios, Iver Heath, Buckinghamshire. The objective of this survey was to provide an ecological assessment of the site and to highlight any potential constraints to
CLIENT: DTZ CONSULTING AND RESEARCH future development proposals for the extension of Pinewood Studios.
The site is situated adjacent and to the east of Pinewood Studios, to the south-west of the M25 motorway and approximately 1km north of the centre of the village of Iver Heath
OUR REF: DTZCON-PINSTU-1480 (centred on OS grid reference TQ 021 844). The site covers an area of approximately 64ha. Habitats within the survey area include semi-improved grassland, hedgerows, dense
and scattered scrub, broadleaved and mixed woodland, ditches, buildings and hardstanding. The M25 motorway marks the north-eastern boundary of the site, Sevenhills Road marks
the northern boundary of the site, Pinewood Road and residential housing marks the MAY 2009 western boundary of the site and Denham Road marks the southern boundary of the site.
A desktop study was undertaken, which included a web based search, a review of planning
policies and relevant Biodiversity Action Plans and data searches provided by Natural England, the Environment Agency, Buckinghamshire County Council and Buckinghamshire
and Milton Keynes Environmental Record Centre.
A survey of the site was conducted on 4 March 2008 using a standard Phase 1 habitat
Written Reviewed + Approved survey method, extended to record provisional signs of and potential for protected or Issue Date of Issue By By notable species. Detailed notes of vegetation, habitats and signs of animal activity were Two 11 May 2009 HG/AC HM recorded. In addition a winter bird scoping survey was also carried out on 4 March 2008.
Following a preliminary assessment of the site, the habitats present are generally of ecological value at a Local and District level (on a scale between International and Site
level).
The following ecological considerations and recommendations are provided:
Retention of important ecological habitat such as woodland, hedgerows, trees and ditches
EXTENDED PHASE 1 HABITAT SURVEY 1 DTZCON-PINSTU-1480 PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Further surveys including: botanical survey; hedgerow survey; bat surveys; CONTENTS badger survey; dormouse survey; breeding and wintering bird surveys; reptile PAGE survey; great crested newt survey; and an invertebrate survey INTRODUCTION ...... 5 Sensitive timing of vegetation removal to take account of species such as hedgehog, harvest mouse and brown hare Objectives of Study ...... 5
General Description ...... 5
NOMENCLATURE ...... 6
METHODS...... 6
Desktop Study ...... 6
Ecological Field Survey ...... 7
Initial Ecological Evaluation ...... 7
RESULTS ...... 8
Desktop Study ...... 8
Ecological Field Survey ...... 13
ECOLOGICAL EVALUATION ...... 23
Preliminary Evaluation of Component Habitats ...... 23
Overall Ecological Evaluation ...... 26
ECOLOGICAL CONSIDERATIONS AND RECOMMENDATIONS ...... 27
INITIAL DESIGN RECOMMENDATIONS ...... 27
FURTHER SURVEYS ...... 28
OTHER RECOMMENDATIONS ...... 30
LIMITATIONS OF SURVEY AND REPORT ...... 30
FIGURE 1: PHASE 1 HABITAT PLAN
FIGURE 2: BIRD SURVEY PLAN
REFERENCES/BIBLIOGRAPHY
EXTENDED PHASE 1 HABITAT SURVEY 2 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 3 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
INTRODUCTION APPENDIX I: SPECIES LIST 1. In February 2008, ecosulis ltd was commissioned by DTZ Consulting and Research APPENDIX II: DEFINING ECOLOGICAL VALUES to undertake an extended Phase 1 habitat survey and wintering bird scoping survey APPENDIX III: AN ECOLOGICAL EVALUATION of land at Pinewood Studios, Iver Heath, Buckinghamshire. The objective of this survey was to provide an ecological assessment of the site and to highlight any APPENDIX IV: ASSESSMENT METHODOLOGIES, RESOURCES AND LEGISLATION potential constraints to future development proposals for the extension of APPENDIX V: LISTS OF BIRDS OF CONSERVATION CONCERN AND LEGISLATION Pinewood Studios.
2. Two members of staff of ecosulis ltd visited the site on 4 March 2008. Access was gained with the permission of the landowner.
3. It is proposed that studios and associated infrastructure will be constructed within the site boundary. The exact proposals are currently unknown.
Objectives of Study
4. This study provides information on the existing ecological conditions at the site and details the methodologies and results of the desktop study, extended Phase I habitat survey and wintering bird scoping survey. The purpose of this report is to identify potential constraints and opportunities that ecology may pose to the proposed development and to identify further ecological studies that may be required to ensure that ecology is fully considered within future development plans.
General Description
5. The site is situated adjacent to the east of Pinewood Studios, to the south-west of the M25 motorway and approximately 1km north of the centre of the village of Iver Heath (centred on OS grid reference TQ 021 844). The site covers an area of approximately 64ha. Habitats within the survey area include semi-improved grassland, hedgerows, dense and scattered scrub, broadleaved and mixed woodland, ditches, buildings and hardstanding. The M25 motorway marks the north-eastern boundary of the site, Sevenhills Road marks the northern boundary of the site, Pinewood Road and residential housing marks the western boundary of the site and Denham Road marks the southern boundary of the site.
6. The majority of the surrounding land includes residential properties to the south and pastoral farmland, woodland and the M25 and M40 motorways to the north, east and west.
EXTENDED PHASE 1 HABITAT SURVEY 4 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 5 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
NOMENCLATURE Legislation, Policy and Biodiversity Action Plans
7. The common name only of flora and fauna species is given in the main text of this 15. This report has taken into account the relevant European and UK legislation and report; however, Latin names are used for species where no common name is policy that affords protection to the natural environment, habitats and species. available. A full species list with Latin names is listed in Appendix I. All plant names 16. Planning policies were reviewed for information on core policies for development follow the nomenclature of Stace (1997). in relation to ecology and biodiversity. County and District/Borough strategies,
METHODS plans and/or frameworks and other development plan documents were included within this review. Desktop Study 17. The UK Biodiversity Action Plan (UK BAP) and the Buckinghamshire BAP (LBAP) Local Records which include action plans for a range of habitats and species, have also been 8. The Buckinghamshire and Milton Keynes Environmental Record Centre reviewed in order to identify nationally and locally important habitats and species (BUCKSMKERC) was asked to provide any information on records of protected and actions proposed to safeguard these features. and/or notable species within a 2km (4km for bats) radius of the site and locations Ecological Field Survey of any statutory and non-statutory site designations in the area. Extended Phase 1 Habitat Survey 9. Buckinghamshire County Council was asked to provide any information on records of Tree Preservation Orders (TPOs) or proposed TPOs within the site, details of 18. Phase 1 Habitat Survey is a survey method and habitat classification system that was any non-statutory wildlife sites within a 2km radius of the site and if the site falls developed by the Nature Conservation Council, now Joint Nature Conservation within a Conservation Area. Committee (JNCC, 2003) to map habitats and land use categories to a ‘consistent level and accuracy’. Vegetation and habitats are mapped using standard colour 10. Natural England and the Environment Agency were contacted to provide codes, allowing rapid visual assessment of the extent and distribution of different information on any records of protected species or designated sites within 2km of habitat types. Where appropriate, Target Notes highlight potential features of the site (4km for bats). interest. An extended Phase 1 habitat survey also records provisional signs of Web Based Search protected or notable species and assesses the potential suitability of the habitats on 11. The ‘Local Live’ website was accessed for aerial views of the site and used as a site and within the accessible surroundings to support such species. visual aid to help put the site into context with its surroundings and to identify any Winter Bird Scoping Survey potential features of interest in the surrounding land. 19. The site was systematically walked so that all habitats on site were visited and all 12. The Multi-Agency Geographical Information for the Countryside (MAGIC) website bird species observed were noted and mapped. Habitats were also described to was consulted for information on statutory site designations in the area. assess their value to birds. 13. The National Biodiversity Network (NBN) website was also consulted for Initial Ecological Evaluation information on records of protected and notable species in the area. 20. Habitat areas and species populations (where appropriate) within the site are Natural Area Profiles assigned preliminary ecological values on a scale between International Value and 14. English Nature (now Natural England) and the Countryside Commission have Negligible Value. The value assigned to habitats and species adopts the jointly produced a series of Natural Area Profiles for 120 areas in England (97 recommendations for evaluating habitats given in the IEEM guidelines for Ecological terrestrial and 23 maritime). The profile of the Natural Area within which the site Impact Assessment (2006). The geographical value categories used in this falls, was referred to for information on characteristic local landscape features and assessment are: International (i.e. Europe), UK, National (i.e. England), Regional used to put the site into context with the local surroundings. (South) County (Buckinghamshire), District (South Buckinghamshire), Local (Iver
EXTENDED PHASE 1 HABITAT SURVEY 6 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 7 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Heath), and Site (i.e. within immediate the zone of influence only). Examples of the 27. BUCKSMKERC also indicate that no non-statutory wildlife sites fall within the site factors that are considered in defining such ecological values are given in Appendix boundary however there is one non-statutory Local Wildlife Site (LWS) and 19 II. Natural processes and interactions between physical and biotic factors are all Biological Notification Sites (BNS) within the 2km search area (see Table 1, below) considered in the assessment. Values are assigned to all habitats likely to be Table 1: A Summary of Non-Statutory Wildlife Sites within the 2km Search Area directly or indirectly affected by the proposed development. Site Location Description 21. The site as a whole has been assessed using criteria set out by Ratcliffe (1977) as a Black park BNS Adjacent to north- A large area of mixed woodland with western corner of site heathland and ponds guide (Appendix III). Long Coppice, Denham 0.2km NE of site Mixed woodland with alder carr RESULTS BNS River Alderbourne east 0.3km N of site A small river with adjacent meadow and Desktop Study of Fulmer BNS pasture Field south of River 0.5km NW of site Acid grassland, some of which waterlogged Local Records Alderbourne BNS Gossams and Rush 0.5km NE of site Mixed woodland with wet areas 22. Information from BUCKSMKERC indicates that no statutory or non-statutory sites Green Wood BNS fall within the site boundary. Four statutory sites including Black Park Site of Wetland north of Long 0.5km NE of site Fen and ponds with areas of rank grassland Coppice BNS Special Scientific Interest (SSSI), Kingcup Meadows and Oldhouse Wood SSSI, Stoke Kingcup Farm Meadow 5 0.6km NE of site Herb-rich acid grassland meadow Common SSSI and Black Park Local Nature Reserve (LNR) fall within the 2km BNS search area. Fulmer Rise Estate BNS 0.6km W of site Mixed woodland with remnants of heath Water Gate Farm, River 1.7km E of site River and adjacent semi-improved 23. Black Park LNR is located adjacent to the north-western corner of the site Colne BNS meadows boundary and comprises woodland, heath, grassland and a lake. Hawkswood Land 0.8km NW of site A hedgerow Hedgerows (south of M40) BNS 24. Black Park SSSI is located approximately 0.6km west of the site and comprises a Kingcup Farm Meadow 4 0.8km NE of site Marshy grassland variety of habitats including dry and wet heath, alder carr, mixed and coniferous BNS woodland and small areas of acid grassland. Locally rare species include dwarf St. Margret’s 0.8km SW of site Acid grassland Churchyard, Iver Heath gorse, trailing tormentil and white sedge. Other nationally rare species include BNS Roesel's bush cricket, hobby, nightjar, adder and grass snake. Southlands Manor LWS 1km W of site Semi-improved grassland, rough grassland and damp rank grassland. Species of note 25. Kingcup Meadows and Oldhouse Wood SSSI is located approximately 0.5km north- include sneezewort, ragged-robin and brown sedge east of the site and comprises an intimate mosaic of habitats adjacent to the River Field by 5-points 1.2km SW of site Neutral grassland Alderbourne, which includes woodland, unimproved pastures and semi and roundabout BNS Bangor’s park Lane BNS 1.3km S of site A small lake with a heronry unimproved meadowland. Oldhouse Wood has been managed in the past as Black park Lake BNS 1.5km SW of site A large lake coppice-with-standards and retains a wide range of native trees and shrubs, along St James’ Churchyard, 1.6km W of site Neutral grassland with many woodland species indicative of ancient woodland. Locally rare species Fulmer BNS include pale sedge, bristle club-rush and herb-Paris. Langley Park BNS 1.7km SW of site Pasture, ponds and trees with some areas of heath. An important site for dead-wood invertebrates 26. Stoke Common SSSI is located approximately 2km west of the site and comprises Hedge west of Billet 1.8km SW of site A parish boundary hedge wet and dry heath with areas of birch, pine and mixed woodland. Species present Farm BNS include green-winged orchid, heath spotted-orchid, dog’s-tooth-violet, bog bush Rowley Wood BNS 2km SW of site Mixed woodland with dominant oak and some pine cricket, great oak beauty moth and chevron moth.
EXTENDED PHASE 1 HABITAT SURVEY 8 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 9 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
28. BUCKSMKERC provided records of notable and protected species within a 2km 32. Natural England does not hold any records of protected species within the data radius of the site (4km for bats). These records of species of note are summarised search area. in Table 2. Web Based Search 29. Table 2: Summary of Notable/Protected and BAP Species within the Search Area 33. MAGIC confirmed information from BUCKSMKERC. No. of records in 2km search Species Closest record to site area 34. NBN gateway holds a number of records of protected and notable species within Slow worm 1 1km SW of site the 10km grid square in which the site lies. These include great crested newt (1.8 Grass snake 2 1.5km SW of site km from the site), wood lark (within 10km of the site), marsh club-moss (within Great crested newt 2 1.9km NW of site 500m of the site), white-clawed crayfish (1.8km from site), brown hare (2km from Kingfisher 3 1.5km SW of site site), otter (within 10km of the site), water vole (within 500m of site), small- Common cuckoo 2 1km W of site flowered catchfly (within 10km of the site), spreading hedge-parsley (within 10km Hobby 3 1km SW of site of the site), starfruit (within 10km of the site), stag beetle (within 10km of the site), Common crossbill 1 1km SW of site Spotted flycatcher 1 0.4km N of site high brown fritillary (within 10 km of the site) and silver-studded blue (within10 km Dartford warbler 1 1km SW of site of the site).
Lapwing 1 0.3km SE of site Natural Area Profiles (English Nature 2003) Fieldfare 2 1km SW of site An ant Lasius brunneus 2 1km SW of site 35. The site lies within the London Basin Natural Area. About one-third of the area is Oak jewel beetle 1 1km SW of site covered by London and the wildlife of the Natural Area is characterised by islands Cardinal click beetle 2 1.2km SW of site of semi-natural habitats. These habitats include large areas of woodland, with Stag beetle 4 0.5km S of site extensive stands of mature beech woods, significant areas of lowland mixed A beetle Scydmaenus 1 1km SW of site rufus deciduous woodland and numerous large wood pastures and parklands. There are Hornet rove beetle 1 1.8km SW of site also notable areas of heathland in the Natural Area.
White admiral 3 1km SW of site Legislation, Policy and Biodiversity Action Plans White letter hairstreak 1 1km S of site Essex skipper 3 0.2km NE of site Legislation and Planning Policies
A fly Ctenophora ornanta 1 1km SW of site 36. A summary of local policies from the South Buckinghamshire Local Plan (adopted Badger 3 1km SW of site January 1999) is outlined below. For a summary of legislation and national policies Noctule 3 1.7km SW of site refer to Appendix IV (for full national details, reference must be made to the Common pipistrelle 6 1.7km SW of site Brown long-eared bat 1 2.3km SW of site policies and acts themselves).
Starfruit 2 0.9km SW of site 37. Policy C10: Key Nature Conservation Sites - Development which would cause demonstrable harm to the whole, or any part of, the following proposed or 30. Buckinghamshire County Council reported that two TPOs affect the site - The designated sites will not be permitted:- Clump, an area of woodland on site adjacent to the M25, and along most of the Internationally designated nature conservation sites (Special Protection Denham Road frontage, including Laurel Court, Furze Cottages and adjoining land. Areas or Special Areas of Conservation); The site does not fall within a Conservation Area. National Nature Reserves; 31. The Environment Agency does not hold any records of white-clawed crayfish, otter or water vole within the data search area. Sites of Special Scientific Interest; EXTENDED PHASE 1 HABITAT SURVEY 10 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 11 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Local Nature Reserves; applicant/landowner entering into a management agreement as set out in Policy C12. the habitat of a protected species The Council will, where appropriate, encourage the enhancement of the nature Designated sites are identified on the Proposals Map. In assessing proposals the conservation value of any land within the District and will specifically encourage the Council will carefully consider the following points:- creation of new habitats. whether the effect on the site or habitat is likely to be significant (in terms 39. The Buckinghamshire LBAP has a number of priority Species Action Plans (SAPs) of the ecological objectives for which the site or species was, or is and Habitat Action Plans (HAPs) for the area, which include HAPs for: calcareous proposed to be, designated/protected), either individually or in grassland; neutral grassland; rivers and streams; lowland heathland and acid combination with other proposals; grassland; standing open water; farmland; fens, marsh, swamp and reedbed; the importance of the site for nature conservation and the need to pay hedgerows; and woodland. SAPs for Buckinghamshire include hornet robberfly, very special attention to the conservation of sites of international and Chiltern gentian, green-winged orchid, wild service tree, marsh fern, juniper, water national significance; vole, striped lynchis moth, Daubenton’s bat, noctule bat, brown long-eared bat,
whether an environmental assessment is needed of the effects of the pipistrelle bat and Natterer’s bat. Objectives of the relevant SAPs and HAPs have proposed development on the site/habitat; been considered within the ‘Ecological Considerations and Recommendations’ section of this report. the availability of alternative suitable sites for the proposed development, or different approaches which would have a lesser or insignificant effect; Ecological Field Survey
if a proposed development is likely to have an effect on a proposed or Extended Phase 1 Habitat Survey designated site of the habitat of a protected species, how that development 40. The following habitat types were recorded on site, and their distribution is mapped and the site / habitat will be managed to ensure that the interests of the on Figure 1. Adjacent habitats are also described. designated site / habitat are to be enhanced and protected; Semi-improved grassland and species-poor semi-improved grassland whether adverse effects of development can be controlled by the Marshy grassland imposition of appropriate conditions to ensure they would not cause unacceptable harm. Amenity grassland 38. Policy C11: Other Nature Conservation Sites - Development will not normally be Broadleaved and mixed woodland
permitted which would be likely, directly or indirectly, to destroy or have a Scrub significantly adverse effect on the nature conservation interest of:- Lines of trees, standard trees and hedgerows (a) any site with significant nature conservation interest which is not included Ditches under Policy C10 above; Buildings and hardstanding (b) any land subject to a management agreement under section 39 of the Wildlife and Countryside Act 1981. Adjacent habitat
Development will only be permitted on, or close to, such sites where the Council Semi-improved grassland and species-poor semi-improved grassland considers the effect on the nature conservation interest of the site could be 41. The majority of the site comprises semi-improved grassland which appears to be effectively limited by the imposition of appropriate conditions or through the utilised by dog walkers and for other recreational purposes. The site comprises Fields 1 to 15, which are shown in Figure 1. Fields 1 – 8 and 10 – 15 comprise EXTENDED PHASE 1 HABITAT SURVEY 12 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 13 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
species poor semi-improved grassland. Field 9 and some sections of Field 8 48. A narrow strip (approximately 5m wide) of young broadleaved woodland plantation comprise semi-improved grassland with a greater floral diversity. is situated adjacent to the northern boundary of the site (Target Note 1, Figure 1). Species present include field maple, ash, rowan, field rose and pedunculate oak. An 42. Species-poor semi-improved grassland on site comprises cock’s-foot, false oat- additional area of young broadleaved woodland plantation (Target Note 2, Figure 1) grass, common bent, creeping bent, Yorkshire-fog, creeping buttercup, tufted is situated within the smaller section of the survey area to the north of the site hair-grass, perennial rye-grass, Timothy, common mouse-ear, dove’s-foot crane’s- comprising willow, field maple, ash and poplar. bill, dandelion, common sorrel, creeping thistle, bramble, spear thistle, mugwort, hogweed, yarrow, ribwort plantain, meadow buttercup and broadleaved dock. 49. A large area of mature (potentially ancient) broadleaved woodland is situated within the central section of the site and is known as The Clump (Target Note 3, 43. Semi-improved grassland on site with a relatively higher species diversity include Figure 1). This area of woodland extends as a narrow strip of woodland to the the following species: red fescue, common bent, annual meadow-grass, crested south and comprises mature pedunculate oak trees with an understory of silver dog’s-tail, cat’s-ear, Yorkshire-fog, cock’s-foot, common knapweed, germander birch, hawthorn, blackthorn, goat willow, hazel (coppice), downy birch, field rose, speedwell, selfheal, daisy, ribwort plantain, common mouse-ear, perforate St John’s- holly and beech. Species within the ground flora include wood dock, bramble, wort, yarrow, parsley piert, common whitlowgrass and mosses including wood meadow-grass, wood-sedge, creeping soft-grass, cleavers, a violet species, Calliergonella cuspidata. The areas of semi-improved grassland with greater floral honeysuckle, red campion, tufted hair-grass, bracken and greater stitchwort. diversity had a short sward height (approximately 2cm) and appeared to be heavily grazed by rabbits. Field 9 also has numerous ant hills. 50. A small area of young to semi-mature broadleaved plantation woodland (Target Note 4, Figure 1) is situated within Field 4 and comprises pedunculate oak, 44. Fields 1, 2, 12, 14 and 15 had a short sward height (15cm - 20cm) at the time of hawthorn, downy birch, willow, holly, wood meadow-grass, tufted hair-grass and survey and the remaining fields had a longer sward height of approximately 30cm. bramble. Some of the fields, including Field 6, appear to be unmanaged due to the presence of scrub and rough grassland mosaic. 51. A large area of mature broadleaved woodland (Target Note 5, Figure 1) is situated adjacent to the south-eastern boundary of the site and comprises mature Marshy grassland pedunculate oak, hazel (coppice), holly, elder and hawthorn. Species within the 45. Two small areas of marshy grassland are situated within Field 8 (refer to Figure 1). ground flora include remote sedge, pendulous sedge, male-fern, broad buckler-fern, Species within these areas include soft-rush, Yorkshire-fog, hard rush, creeping hart’s-tongue, wood avens and a violet species. buttercup and a sedge species. These areas were wet underfoot and had a sward 52. An area of mixed woodland is situated adjacent to the south-eastern boundary of height of approximately 30cm. the site (Target Note 6, Figure 1) and comprises mature Scot’s pine, yew, holly, Amenity grassland beech, rhododendron, bramble, common nettle and remote sedge. 46. Three areas of amenity grassland are present within the survey area and all are 53. Standing and fallen dead wood exists within these habitat types. associated with residential properties. These areas were not surveyed directly Scrub though species noted from a distance include: perennial rye-grass, daisy, dandelion and ribwort plantain. The sward height of this habitat type was approximately 5cm 54. Scattered scrub and dense scrub is situated throughout the site and comprises – 10cm. bramble, goat willow, hawthorn, blackthorn, dogwood and oak saplings.
Broadleaved and mixed woodland Lines of trees, standard trees and hedgerows
47. Five areas of broadleaved woodland are situated within the survey area along with a 55. Lines of trees and hedgerows mark many of the field boundaries throughout the single area of mixed woodland. site. Standard trees are situated within many of the hedgerows.
EXTENDED PHASE 1 HABITAT SURVEY 14 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 15 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
56. Lines of trees on site include mature pedunculate oaks with an understory of Adjacent habitat hawthorn and bramble. 65. A narrow strip of scrub and young plantation woodland lies between the site and 57. There are mature and young hedgerows on site (refer to Figure 1). The young the M25 motorway comprising species such as hawthorn, field maple, dog-rose and hedgerows are approximately 1m in height and 70cm wide with hawthorn, dog- hazel. rose, blackthorn and field maple. The more mature hedgerows on site vary in size, 66. Residential houses and gardens and the Pinewood Studios lies to the south of the though on average are 3m wide and 3m high. Species present within hedgerows on site which comprise amenity planting and some mature trees. site include hawthorn, blackthorn, sycamore, hazel, beech, willow, ash, dog-rose, 67. Black Park LNR lies adjacent to the northern corner of the site and comprises holly and pedunculate oak with a ground flora of honeysuckle, ivy, primrose, scaly mature woodland with species such as pedunculate oak, holly, downy birch and male-fern, bluebell, foxglove and common nettle. bramble. 58. The vast majority of the hedgerows within the survey area are in a good state of Field Observations repair and provide suitable barriers to livestock. Flora 59. Mature standard trees within hedgerows include pedunculate oak, ash and sycamore. 68. Bluebell, a species listed upon Schedule 8 of the Wildlife and Countryside Act 198, was identified during the survey within hedgerow habitat, though is likely to also 60. Standing and fallen dead wood exists within these habitat types. occur within areas of woodland. This species is protected from collection from the Ditches wild. 61. Three sections of wet ditch are present within the survey area. The wet ditch 69. No other notable species of flora were observed during the survey however the located adjacent to the west of Field 9 is well shaded by adjacent scrub and survey was not conducted within the optimal botanical survey season. It is unlikely woodland and comprises shallow banks with woodland flora (Target Note 7, Figure that notable species of flora will be present within scrub, species-poor semi- 1). This ditch was approximately 30cm wide and 5cm deep during the survey improved grassland, amenity grassland, young hedgerows and within residential period with a low to moderate flow and a silty substrate. areas on site due to the improved nature of these habitats. However notable floral 62. The flowing ditch adjacent to the southern boundary of the site is also well shaded species may occur within woodland habitat, mature hedgerows, lines of trees, semi- by adjacent woodland and the banks are also colonised by woodland flora such as improved grassland and marshy grassland on site. pendulous sedge and ivy. This ditch (Target Note 8, Figure 1) is approximately 2m 70. Based on a preliminary survey of the hedgerows on site, several of the hedgerows wide and 10cm deep with shallow banks and a silty substrate. may be considered, under the Hedgerow Regulations Act 1997, as being of wildlife 63. Small sections of ditch adjacent to the western site boundary (Target Note 9, / landscape importance (note that a full assessment of the hedgerows was not Figure 1) surround a small area of hardstanding. These ditches are approximately undertaken). 1.5m in width, 10m long and 30cm deep. Bulrush is present within these ditches. 71. No invasive species listed on Schedule 9 of the amended Wildlife and Countryside Buildings and hardstanding Act 1981 were noted on site at the time of the survey.
64. Three small residential areas fall within the site boundary, a farm house and Mammals associated buildings is situated within the northern corner of the site, two blocks of Badger flats are situated adjacent to the south-eastern boundary of the site and a semi- 72. Five entrance holes (Target Note 10, Figure 1) were noted adjacent to the detached house is situated within the southern corner of the site. southern boundary of Field 9. The size of the entrances and spoil heaps indicate
they could be attributable to badger, but there did not appear to be recent signs of
EXTENDED PHASE 1 HABITAT SURVEY 16 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 17 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
activity by badgers. Signs of rabbit were evident at the entrances. No other recent 80. The shallow ditches on site provide a sub-optimal foraging resource for otter as signs of badger activity, such as prints, latrines, foraging signs or hairs, were noted they are unsuitable to support sufficient prey items. In addition it is also unlikely during the survey. The site provides suitable foraging habitat in the form of that otters commute along ditches within the site as they are relatively disjunct in grassland and berry bearing scrub species for badger. According to BUCKSMKERC nature and also there are no substantial watercourses within 2km of the site and badger have been recorded 1km south-west of the site. the site is therefore unlikely to act as a suitable corridor for this species.
Bats Other Mammals
73. Numerous mature and semi-mature trees on site are considered to offer suitable 81. Hedgerows, grassland and scrub on site offer suitable habitat for hedgehogs, brown roosting habitat for bats due to the presence of cracks, rot holes splits and ivy hare and harvest mouse (UK BAP species). coverage. In addition buildings within and adjacent to the survey area may also 82. Habitat of potential value to foraging and sheltering hedgehog is present on site in provide suitable habitat for roosting bats. the form of scrub, hedgerows and grassland. BUCKSMKERC and the NBN
Gateway website did not provide any records of this species within the survey area. 74. Hedgerows, woodland, lines of trees, scrub, semi-improved pasture and ditches on site offer suitable commuting paths and foraging habitat for bats. 83. The NBN Gateway website provided a record of brown hare from a location approximately 2km from the site. The site is suitable for brown hare due to the 75. According to BUCKSMKERC several species of bat have been recorded within the dominant grassland habitat. local area including noctule (1.7km south-west of the site), common pipistrelle (1.7km south-west of the site) and brown long-eared bat (2.3km south-west of the 84. Although no records of harvest mouse were provided by BUCKSMKERC and the site). NBN Gateway grassland and scrub on site offer suitable habitat for this species.
Dormouse Reptiles
76. The hedgerow, woodland and scrub habitats on site are considered to be suitable 85. Habitat of potential value to foraging, commuting and hibernating reptiles includes for dormouse. In addition aerial photo interpretation reveals the presence of other scrub, hedgerows and semi-improved grassland. Ditches provide suitable habitat areas of woodland with potential suitability for dormouse are situated to the north, for amphibian prey, especially for grass snake. Habitats on site are suitable to south, west and east of the site. Hedgerows provide connectivity to the majority support the more common species of reptile, namely common lizard, grass snake of these areas. Information provided by the NBN Gateway website or and slow worm. BUCKSMKERC provided records of slow worm (the closest of BUCKSMKERC did not include records of dormouse. which is 1km south-west of the site) and grass snake (1.5km south-west of the site) within the 2km data search area. In addition adder has been recorded within Black Water Vole Park SSSI, 0.6km west of the site. 77. According to the NBN Gateway water vole has been recorded within 500m of the Amphibians site boundary. BUCKSMKERC did not provide any records of this species. 86. Two palmate newts were observed during the survey within the ditch highlighted 78. No signs of water vole activity were identified during the site survey. Ditches on by Target Note 9 (Figure 1). Great crested newts have been recorded 1.9km site are not considered to offer suitable water vole habitat due to their limited north-west of the site according to BUCKSMKERC. extent, isolated nature, shallow bank profile and the lack of potential sheltering and foraging habitat. 87. Habitat suitable for breeding, foraging and hibernating amphibians is present on site. Of the ditches within the site boundary the ditch highlighted by Target Note 9, Otter Figure 1, is considered to offer suitable breeding habitat for amphibians, specifically 79. According to the NBN Gateway, otter has been recorded within 10km of the site great crested newt, due to the presence of standing water. The other ditches are (the exact location of this record is unknown). of low to moderate flow rate and as such are considered unsuitable breeding
EXTENDED PHASE 1 HABITAT SURVEY 18 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 19 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
habitat. In addition the ditch highlighted by Target Note 9 offers suitable egg-laying Winter Bird Scoping Survey substrate and foraging and sheltering habitat (marginal and aquatic vegetation). The 94. In total, 30 species of birds were recorded during the survey, which include four other ditches are shaded and therefore are not colonised by aquatic or marginal Red Listed Birds of Conservation Concern (BOCC) species, seven Amber Listed vegetation. BOCC species and 19 Green Listed species (refer to Table 3 below, Figure 2 and 88. Aerial photo interpretation and a review of OS maps reveal the presence of Appendix V for further details on the criteria for these BOCC lists). Furthermore, additional ponds within the Pinewood Studio complex (250m from the site one Schedule 1 species (refer to Appendix V for information) was present, namely boundary). In addition, although not visible from aerial photo interpretation, redwing. Skylark and song thrush are listed in the UKBAP. National status is based garden ponds location within the residential area to the south of the site, if present, on BTO Bird Trends and BTO Wetland Bird Survey 2004/5 data. may offer suitable habitat for amphibians. Table 3. Bird species recorded during winter bird scoping report 89. Woodland, hedgerows, semi-improved grassland, lines of trees and scrub offer suitable terrestrial habitat for amphibians. Bird Species Conservation National Status BTO Status Code Invertebrates (refer to Figure 2 90. Habitats suitable for invertebrates are present on site in the form of flowering for locations) plants, mature trees, dead wood and leaf litter. The structural diversity on site is Blue tit Green Long term shallow BT likely to provide suitable habitat to a variety of invertebrates. population increase Blackbird Green Long term shallow decline B. 91. The site also offers suitable habitat for several LBAP and notable invertebrates Black-headed gull Amber BH Coal tit Green Common breeding CT including the Nationally Scarce ant species Lasius brunneus, which feeds on the resident Collared dove Green Common resident CD decaying heartwood of trees, the LBAP oak jewel beetle, which requires mature Carrion crow Green Long-term rapid increase C. oak trees, the LBAP cardinal click beetle, which requires rotting oak heartwood, Chaffinch Green Long-term shallow CH increase the UK BAP stag beetle, which requires dead wood, especially oak, the Red Data Common gull Amber Common winter visitor CG book beetle Scymaenus rufus, which inhabits veteran trees and decaying wood, the and passage migrant Dunnock Amber Long-term moderate D. Red Data Book hornet rove beetle which requires light, free draining habitat with a UK BAP decline Goldfinch Green Fluctuating with no long- GO variety of dung (including rabbit droppings, which is present on site) of different term trend ages and the LBAP white admiral butterfly, which inhabits woodland rides with Great tit Green Long-term shallow GT increase honeysuckle. All those species listed above have been recorded within the 2km Greenfinch Green Long-term shallow GR increase search area. Green woodpecker Green long-term rapid increase G. House sparrow Red Rapid long term decline HS 92. The Nationally Scarce Roesel’s bush cricket, a cricket occurring within Black Park UK BAP SSSI, 0.6km from the site, inhabits wet grassland and may therefore occur within Jackdaw Green Long-term moderate JK increase the marshy grassland on site. Kestrel Amber Long-term moderate K. decline 93. The LBAP species hornet robber-fly and the UK BAP pearl-bordered fritillary, Magpie Green Long-term rapid increase MG Meadow pipit Amber Long-term moderate MP although not recorded in the local area, may also occur on site due to the presence decline of suitable habitat. The hornet robber-fly, like the hornet rove beetle, requires free Nuthatch Green England, rapid increase NH Pheasant Green Long-term moderate PH draining habitat with a variety of dung (including rabbit droppings, which is present increase on site) of different ages and the pearl-bordered fritillary inhabits woodland Redwing Amber long-term rapid decline RE Schedule 1 W&CA clearings with bracken and violets. Robin Green long-term moderate R. EXTENDED PHASE 1 HABITAT SURVEY 20 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 21 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
increase wet grassland that offers thick vegetation for cover and soft ground and wet flushes Siskin Green long-term probable SK increase for foraging. This species prefers areas that have easy access to shallow pools, Skylark Red England long-term rapid S. which are utilised as a foraging resource. It is unclear if the wet flushes are present UKBAP decline Song thrush Red long-term rapid decline ST throughout the year, but at the time of the survey the habitat appeared suitable for UKBAP a range of wader species. Snipe Amber UK long-term trend SN probable decline Sparrow hawk Green Long-term rapid increase SH 99. Black Park SSSI lies approximately 0.6km west of the site and is designated in part Starling Red Long-term rapid decline SG for breeding and winter bird assemblages including sparrowhawk, coal tit, goldcrest, UK BAP Wood pigeon Green Long-term rapid increase WP firecrest, tree creeper and tree pipits. Two of these species, namely coal tit and Wren Green Long-term moderate WR sparrow hawk, were recorded during the survey and the site is considered suitable increase to offer year round habitat for goldcrest, firecrest and treecreeper. Tree pipits are 95. The site offers a good diversity of habitats providing shelter and foraging generally associated with open heathland and conifer plantations, which are not opportunities for a range of birds species. The five areas of woodland provide present on site.
habitat for woodland birds including sparrow hawk, tit species and nuthatch, 100. Hobby and the nightjar are also noted within the Black Park SSSI designation, but recorded during the survey. are summer migrants to Britain. The site offers suitable foraging for hobby in the 96. The grassland with surrounding hedgerows provide optimum habitat for farmland form of woodland and marshy areas, which are likely to provide habitat for large and open grassland species with scattered scrub and woodland providing additional insect prey. The site is of less value to nightjar, which prefer heathland, moorland, cover and adding value to the site in the local context. A single song thrush (Red open woodland with clearings, and recently felled conifer plantations.
List BOCC and UKBAP) was observed during the survey and was associated with 101. Overall, a moderate diversity of bird species, including wintering and breeding the hedgerows to the north-west of the site. Two individual skylark (Red Listed species were recorded using the site during the one survey undertaken. Some of BOCC and UKBAP) were noted singing within grassland on site. The grassland the bird species associated with the neighbouring designated sites were also found offers suitable nesting habitat for this species. A small flock of starling (Red Listed to be using the site as well as more common species. BOCC and UKBAP) were also recorded foraging within the grassland. The mosaic ECOLOGICAL EVALUATION habitat also provides good habitat for wintering thrushes including redwing (Amber Listed BOCC and Schedule 1 species; refer to Appendix V for details), which forage Preliminary Evaluation of Component Habitats
on open grassland and utilise fruiting scrub and hedgerows for foraging and shelter. 102. The table below (Table 4) provides a preliminary evaluation of habitats on site and 97. The range of habitats on site offer important habitat for bird species during winter adjacent habitats, based upon relevant planning policies, the UK / LBAP and the and during the breeding season. The lines of trees, scattered scrub and hedgerows results of the ecological field survey. These values may change following further on site provide connectivity throughout the site and into the wider surroundings. surveys (see recommendations below).
The majority of the passerines rely on the hedgerows for shelter and for foraging, including finches, tits and thrushes. Some species may be resident on site and will
use the vegetation all year round; other species may be transient, visiting the site or passing through, therefore using the vegetation as stepping-stone habitat. This is likely to be the case with the flocks of siskin and meadow pipit that were recorded; during the winter months these species are very mobile and roam the countryside.
98. A single snipe (Amber Listed BOCC) was the only wader represented on site and was observed within the marshy grassland. This species was associated with the EXTENDED PHASE 1 HABITAT SURVEY 22 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 23 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Table 4. Initial Ecological Evaluation of Habitats birds and suitable habitat for LBAP, UK BAP and notable invertebrate species Preliminary Habitat Qualifying Criteria Woodland is an LBAP habitat Ecological Value
Semi-improved Provides suitable habitat for foraging Local Value Scrub This habitat type is extensive throughout Local Value grassland and hedgehog, brown hare, invertebrates (UK the site species-poor BAP, LBAP and notable species), birds, Provides suitable habitat for nesting birds, semi-improved badger, harvest mouse, foraging bats, dormouse, foraging and hibernating grassland reptiles and amphibians. Species-poor reptiles and amphibians, harvest mouse semi-improved grassland habitat is and foraging habitat for badger relatively common and widespread within Tree lines, Provide a network of linear features the surrounding area, though semi- hedgerows and across the site improved grassland with greater species standard trees Tree lines: Suitable habitat for diversity is unlikely to be common within District Value the local area commuting and foraging bats, nesting
birds, commuting badger, commuting, Neutral grassland is a LBAP and UK BAP foraging and hibernating reptiles and habitat amphibians and suitable habitat for UK, Marshy grassland Although limited in extent this habitat Local Value LBAP and notable species of invertebrate
provides suitable habitat for wintering Hedgerows: Provide green corridors and birds, invertebrates (including Roesel’s link to a network of habitats within the bush cricket), reptiles and amphibians. wider area. Provides suitable habitat for Local Value
Potential to support notable floral species hedgehog, harvest mouse, invertebrates, foraging badger, dormouse, foraging and Fens, marsh, swamps and reedbeds are LBAP habitats nesting birds, foraging and commuting habitat for bats and foraging and Amenity grassland Low coverage on site adjacent to Site Value hibernating habitat for reptiles and buildings amphibians
Suitable habitat for foraging hedgehogs, Hedgerows are a LBAP habitat type. badgers, invertebrates and birds Hedgerows on site may also be Broadleaved Patches of woodland connected by District Value considered to be of wildlife and landscape District Value woodland and hedgerows importance under the Hedgerow
mixed woodland Regulations Act 1997 and therefore could Suitable habitat for notable floral species, also be a UK BAP habitat type dormouse, hibernating reptiles and
amphibians badger, roosting, foraging and Standard trees: Provide suitable habitat
commuting bats, foraging and nesting for invertebrates, foraging, and
EXTENDED PHASE 1 HABITAT SURVEY 24 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 25 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
hibernating dormouse, foraging and 104. Naturalness and fragility are represented in the form of lines of mature trees, District Value nesting birds, foraging and roosting woodland and hedgerows.
habitat for bats and hibernating habitat 105. Habitat rarity on the site is low with no rare habitats noted. However hedgerows for reptiles and amphibians such as great on site may be considered under the Hedgerow Regulations Act 1997 to be of crested newt. Dead wood provides ecological and landscape importance. In addition hedgerows (and standard trees) suitable habitat for LBAP, UK BAP and and neutral grassland are both LBAP habitats present on site. notable invertebrate species 106. The ecological interest of the site is related to: Standard trees within hedgerows are a The proximity of the site to designated sites, namely Black Park LNR and LBAP habitat type Black Park SSSI, and the flora/fauna they support Ditches Provides a small contribution to the Local Value The potential of the hedgerows on site to be of wildlife and landscape value network of linear features on site under the Hedgerow Regulations Act (1997) and therefore a UK BAP habitat Suitable habitat for invertebrates, foraging The potential of the grassland and woodland on site to have botanical habitat for bats and breeding habitat for interest amphibians The presence of a number of potential LBAP habitats including grassland, Standing open water and rivers and woodland, hedgerows and their associated standard trees, and ditches streams are LBAP habitats The site’s suitability to support protected species, including badger, Buildings and Suitable roosting habitat for bats and Site Value dormouse, bats, reptiles and amphibians hardstanding nesting habitat for birds Black Park LNR: Suitable habitat for The suitability of the site to support notable species, including LBAP Adjacent habitat Local Value Roesel's bush cricket, hobby, nightjar, species, such as invertebrates, hedgehog, harvest mouse and brown hare
adder and grass snake The value of the site to wintering birds, including those associated with the
Hedgerows and semi-improved grassland: neighbouring designated sites, as well as common bird species, for nesting and Suitable for local wildlife including birds, Local Value feeding reptiles, amphibians and dormouse 107. Following a preliminary assessment of the site, the habitats present are generally of
Margins of M25: Suitable habitat for Local Value ecological value at a District to Local level. invertebrates, nesting birds, dormouse, ECOLOGICAL CONSIDERATIONS AND RECOMMENDATIONS reptiles and amphibians and foraging Initial Design Recommendations habitat for bats
108. It is recommended that trees, woodland areas, hedgerows, ditches and scrub are Overall Site Evaluation retained on site wherever possible and are managed under a sensitive management regime for wildlife. A buffer between these features and the development footprint 103. The site is of large size and comprises semi-improved grassland, amenity grassland, is also recommended to retain commuting and foraging habitat for wildlife and marshy grassland, hedgerows, ditches, standard trees, scrub, hardstanding and protect these more sensitive habitats to disturbance. buildings. Species diversity is moderate due to the presence of a diversity of habitats.
EXTENDED PHASE 1 HABITAT SURVEY 26 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 27 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
109. It is also recommended that grassland of potential botanical interest, in particular Dormouse – Due to the presence of suitable habitat for dormouse, such as Fields 8 and 9 and the areas of marshy grassland, are retained on site where hedgerows and woodland on the site, and the presence of hazel, it is possible (subject to further surveys). recommended that a dormouse survey in the form of a hazelnut search is
110. Dead wood (standing and fallen) should be retained on site, unless considered to undertaken. This should be undertaken in October to December, but be a health and safety risk, to continue to provide a variety of habitats within the could be conducted at other times of the year site boundary. Breeding Birds – Due to the presence of suitable nesting habitat for a
Further Surveys number of rare species, the presence of a number of breeding species recorded during the survey and the close proximity of Black Park SSSI, Botanical Survey – Due to the presence of grassland (Fields 8 and 9 and which is designated in part for breeding birds, a breeding bird survey should areas of marshy grassland), and woodland (Target Notes 3, 5 and 6) of be undertaken of the site. This survey should follow British Trust for potential botanical interest, it is recommended that a botanical survey is Ornithology (BTO) methods, which consist of three visits, between April undertaken of these areas. This survey should be undertaken between May and June and July (prior to a summer cut of the grassland) Wintering Birds – Due to the presence of suitable habitat on site, the Hedgerow Survey – Due to the presence of hedgerows that may be presence of several wintering species recorded during the survey and the important under the Hedgerow Regulations Act 1997, it is recommended close proximity of Black Park SSSI, which is designated in part for wintering that a hedgerow survey be undertaken of the hedgerows on site. This birds, a wintering bird survey should be undertaken of the site. This survey survey should be undertaken in April/May would follow BTO methods and would consist of two visits per month Badger Survey – Due to the presence of a badger sett (Target Note 10, from September to March Figure 1) and suitable habitat on site, it is recommended that a badger Reptile Survey – Due to the presence of grassland, scrub, hedgerows and survey is carried out on site. This can be undertaken at any time of the woodland edges, which offer suitable habitat for reptiles, and records of year, but is more effective in spring when badger activity is at its peak and reptiles occurring in the area, it is recommended that a reptile survey is vegetation is less dense undertaken. This should be undertaken between April to October, with Bat Activity Surveys– It is recommended that bat activity surveys are the optimum months being April/May and September undertaken out on site to determine if the site provides valuable foraging Amphibians – Due to the presence of suitable breeding habitat on and off and commuting corridors for local bat populations. These surveys should site, a great crested newt survey is recommended. This should be be undertaken between May and September undertaken between mid-March and mid-June in suitable weather Bat Tree and Building Surveys - Should trees and/or buildings on site be Invertebrates – Due to the presence of suitable habitat for a number of Red affected by the development, it is recommended that further surveys be Data Book and UK BAP invertebrate species recorded in the local area, it undertaken on these features. Internal inspections of buildings and tree is recommended that an invertebrate survey is carried out. It is assessments can be undertaken at any time of the year, however if recommended that the survey includes three site visits; one timed in spring, emergence/dawn swarming surveys are required, these should be one timed in summer and one timed in autumn undertaken between May and September. Should any bat roosts be affected by the development a licence from Natural England may be necessary
EXTENDED PHASE 1 HABITAT SURVEY 28 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 29 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Other Recommendations undertaken and all necessary further surveys completed. Likewise the ecological considerations at this stage are not necessarily final and may be subject to change 111. Hedgerows, woodland, scrub and semi-improved grassland provide suitable foraging or additional proposals made following the results of further surveys and and sheltering habitats for hedgehog (a UK BAP species). If areas of suitable development plans. hedgehog habitat are due to be lost under the current development proposals it is recommended that whilst these habitats are removed care is taken and that an 117. The behaviour of animals can be unpredictable and may not conform to standard ecologist is present to carry out a hand search to find and relocate any hedgehogs patterns recorded in current scientific literature. This report therefore cannot present. In addition it is recommended that vegetation clearance / removal of leaf predict with absolute certainty that animal species will occur in apparently suitable litter etc is not carried out in winter when this species hibernates. Any hedgehogs locations or habitats or that they will not occur in locations or habitats that appear found should be relocated to suitable habitat on site or immediately adjacent to the unsuitable. site. 118. The data search can only provide information on species already recorded and 112. Brown hare (a UK BAP species) has been recorded 2km from the site boundary cannot be taken to represent a complete overview of all species present in the and the site offers suitable habitat for this species. Due to the presence of mixed survey site. agricultural land within the surrounding area, it is unlikely that local populations of this species will be affected by development of the site in the long-term, however it is recommended that an experienced ecologist carries out a hand search prior to vegetation clearance (if carried out between February and August) to locate any leverets (young hares) in nests if present. Leverets would be relocated to a suitable undisturbed site, as close to the original nest site as possible.
113. Suitable habitat for harvest mouse (a UK BAP species) is present on site. It is therefore recommended that areas of rough grassland are retained where possible. If this is unavoidable it is recommended that those areas due for removal are maintained in an unfavourable status for harvest mice (i.e. kept at a short sward height) prior to removal. In addition it is recommended that areas of rough grassland maintained on site are managed for harvest mice and are not cut back prior to the end of the breeding season which lasts from May to October.
LIMITATIONS OF SURVEY AND REPORT
114. This report records wildlife found during the survey and anecdotal evidence of sightings. It does not record any plants or animals that may appear at other times of the year and were therefore not evident at the time of visit. Some species that might use the Site or be apparent at other times of year, or only in certain years, would not have been detected.
115. Due to the presence of dense hedgerows and scrub not all sections of the site could be accessed fully.
116. This report provides provisional ecological baseline for the site and should not be considered to be conclusive until the ecological considerations have been EXTENDED PHASE 1 HABITAT SURVEY 30 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 31 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS Field 14 1 Field 13 Field 15 2
7 2 Field 9 N
x Figure x x Field 8 10
x x x ltd x Fax: 01225 874554 3 sulis co e Field 12 Bath, BA2 9BT Pinewood Studios Studios Pinewood Bird Scoping Map Scale SCHEMATIC ONLY Field 6 Field 5 DTZ Pinewood Land Ownership BTO Species Code (refer to Table 1 in main text) *Colour of bird recording refers to BOCC designations The Rickyard, Newton St Loe, Newton St Loe, The Rickyard, Tel: 01225 874040 S. ecological and arboricultural consulting consulting arboricultural ecological and 2008
Field 11 March Key Third Party Land Project Title Date Client Client
Field 2 x x x Field 10 x x x x Field 1 x x x x x 9 x x x x x BT GR R. MG GT WP R. B.
x 2
Field 7 x R.
4 2 GT
x BT x WR x GT GT x 3 x BT BT x x 3
x MP x x x x 10 x WR x x x x C. WP Field 4 BT MG CG 6 6 WP D R. J C. R. GR HS HS R.
8 WP
Reproduced from Ordnance Survey mapping of the CT GT SH Field 3 BT BT Controller of Her Majesty’s Stationary Office © Crown 2 Copyright AL 5 D. GT WR CD CD MG 10 CG GR MG G. WP R. SG
K. SN CH 4 B.
Key H. BT WP MG
ecosulis ltd GT D. SK GT ecological and arboricultural consulting 20 BT Site boundary The Rickyard, Newton St Loe, GO 2 MP G. NH 2 Bath, BA2 9BT S.
Semi-improved grassland GO Tel: 01225 874040 Fax: 01225 874554 RE
Species-poor semi-improved grassland GO C. Client B. ST
R.
Marshy grassland S.
BH MG
Project Pinewood Studios PH
Broadleaved woodland GT 2 CH mapping of the Mixed woodland y Title Phase 1 Habitat Plan MG
Dense scrub Fence WP 30 Date Scale Figure CH x Scattered scrub Hardstanding March SCHEMATIC 1
Line of mature trees 2008 ONLY GT
Buildings C. WR 3
Hedgerow Mature tree standards CH Young hedgerow
Target Note N Controller of Her Majesty’sStationary Office © Crown Copyright AL Ditch Reproduced from Surve Ordnance Amenity grassland ______ecosulis ltd ______ecosulis ltd _
REFERENCES/BIBLIOGRAPHY
APPENDIX I: SPECIES LIST Buckinghamshire County Council (1996) Buckinghamshire Biodiversity Action Plan. Accessed at: http://www.ukbap.org.uk/lbap.aspx?ID=448 Flora
English Nature (2003) Science and Research at www.english-nature.org.uk Updated in Common Name Latin Name 2003. Annual meadow-grass Poa annua HMSO (1981) Wildlife and Countryside Act 1981 (and subsequent amendments). HMSO Ash Fraxinus excelsior HMSO (1992) Protection of Badgers Act 1992 HMSO Beech Fagus sylvatica HMSO (1994) The Conservation (Natural Habitats, &c.) Regulations 1994 HMSO Blackthorn Prunus spinosa HMSO (1995) Biodiversity. The UK Steering Group Report Bluebell Hyacinthoides non-scripta HMSO (1997) The Hedgerow Regulations 1997 HMSO Bracken Pteridium aquilinum HMSO (2000) The Countryside and Rights of Way Act 2000 HMSO Bramble Rubus fruticosus agg. Institute of Ecology and Environmental Management (2006) Guidelines for Ecological Bristle club-rush Isolepis setacea Impact Assessment in the United Kingdom Website – www.ieem.co.uk Broad buckler-fern Dryopteris dilatata Joint Nature Conservation Committee (JNCC) (2003) Handbook for Phase I Habitat Broadleaved dock Rumex obtusifolius Survey – a Technique for Environmental Audit. JNCC London. Second Edition. (Formerly Nature Conservation Committee, [1990]) Brown sedge Carex disticha
Local Live Website at http://local.live.com/?v=2&cid=CA9174951359E039!104 Bulrush Typha latifolia
Multi-Agency Geographical Information for the Countryside (MAGIC) Website Cat’s-ear Hypochaeris radicata at www.magic.gov.uk Cleavers Galium aparine
National Biodiversity Network (NBN) Website at www.nbn.org.uk Cock’s-foot Dactylis glomerata
Ratcliffe, D. (1977) A Nature Conservation Review. Volume 1. CUP Common bent Agrostis capillaris South Buckinghamshire Council (1999) South Buckinghamshire Local Plan (adopted Common knapweed Centaurea nigra 1999). Accessed at: http://www.cartoplus.co.uk/south_bucks/text/00cont.htm) Common mouse-ear Cerastium fontanum Stace, C. (1997) New Flora of the British Isles 2nd Edition. Cambridge University Press Common nettle Urtica dioica TSO (2005) Planning Policy Statement 9: Biodiversity and Geological Conservation. TSO Common sorrel Rumex acetosa TSO (2006) Natural Environment and Rural Communities Act TSO Common whitlowgrass Erophila verna TSO (2007) The Conservation (Natural Habitats, &c.) (Amendment) Regulations 2007 TSO Creeping bent Agrostis stolonifera
Creeping buttercup Ranunculus repens
Creeping soft-grass Holcus mollis
EXTENDED PHASE 1 HABITAT SURVEY 32 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 33 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Creeping thistle Cirsium arvense Male-fern Dryopteris filix-mas
Crested dog’s-tail Cynosurus cristatus Marsh club-moss Lycopodiella inundata
Daisy Bellis perennis Meadow buttercup Ranunculus acris
Dandelion Taraxacum officinalis a moss Calliergonella cuspidata
Dog-rose Rosa canina Mugwort Artemesia vulgaris
Dog’s-tooth-violet Ophioglossum vulgatum Pale sedge Carex pallescens
Dogwood Cornus sanguinea Parsley-piert Aphanes arvensis
Dove’s-foot crane’s-bill Geranium molle Pedunculate oak Quercus robur
Downy birch Betula pubescens Pendulous sedge Carex pendulous
Dwarf gorse Ulex minor Perennial rye-grass Lolium perenne
False oat-grass Arrhenatherum elatius Perforate St John’s-wort Hypericum perforatum
Field maple Acer campestre a pine Pinus sp.
Field-rose Rosa arvensis a poplar Populus sp.
Foxglove Digitalis purpurea Primrose Primula vulgaris
Germander speedwell Veronica chamaedrys Ragged-robin Lychnis flos-cuculi
Goat willow Salix caprea Red campion Silene dioica
Greater stitchwort Stellaria hollostea Red fescue Festuca rubra
Green-winged orchid Orchis morio Remote sedge Carex remota
Hard rush Juncus effusus a rhododendron Rhododendron sp.
Hart’s-tongue fern Phyllitis scolopendrium Ribwort plantain Plantago lanceolata
Hawthorn Crataegus monogyna Rowan Sorbus aucuparia
Hazel Corylus avellana Scaly male-fern Dryopteris affinis
Heath spotted-orchid Dactylorhiza maculata Scot’s Pine Pinus sylvestris
Herb Paris Paris quadrifolia Selfheal Prunella vulgaris
Holly Ilex aquifolium Silver birch Betula pendula
Hogweed Heracleum sphondylium Small-flowered catchfly Silene gallica
Honeysuckle Lonicera periclymenum Sneezewort Achillea ptarmica
Ivy Hedera helix Soft-rush Juncus effusus
EXTENDED PHASE 1 HABITAT SURVEY 34 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 35 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Spear thistle Cirsium vulgare Fauna Spreading hedge parsley Torilis arvensis Common Name Latin Name Starfruit Damasonium alisma Adder Viper berus Sycamore Acer pseudoplatanus an ant Lasius brunneus Timothy Phleum pratense Badger Meles meles Trailing tormentil Potentilla anglica a beetle Scydmaenus rufus Tufted hair-grass Deschampsia flexuosa Blackbird Turdus merula a violet Viola sp. Black-headed gull Larus ridibundus White sedge Carex curta Blue tit Cyanistes caeruleus Wood avens Geum urbanum Bog bush cricket Metrioptera brachyptera Wood dock Rumex sanguineus Brown hare Lepus europaeus Wood meadow-grass Poa nemoralis Brown long-eared bat Plecotus auritus Wood sedge Carex sylvatica Cardinal click beetle Brachygonus ruficeps Yarrow Achillea millefolium Carrion crow Corvus corone Yew Taxus baccaca Chaffinch Fringilla coelebs Yorkshire-fog Holcus lanatus Chevron moth Eulithis testata
Coal tit Periparus ater
Collared dove Streptopelia decaocto
Common crossbill Loxia curvirostra
Common cuckoo Cuculus canorus
Common gull Larus canus
Common pipistrelle Pipistrellus pipistrellus
Dartford warbler Sylvia undata
Daubenton’s bat Myotis daubentonii
Dormouse Muscardinus avellanarius
Dunnock Prunella modularis
Essex skipper Thymelicus lineola
EXTENDED PHASE 1 HABITAT SURVEY 36 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 37 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Fieldfare Turdus pilaris Redwing Turdus iliacus
Goldfinch Carduelis carduelis Robin Erithacus rubecula
Grass snake Natrix natrix Roesel’s bush cricket Metrioptera roeselii
Great crested newt Triturus cristatus Silver-studded blue Plebeius argus
Great oak beauty moth Hypomecis roboraria Siskin Carduelis spinus
Great tit Parus major Skylark Alauda arvensis
Greenfinch Carduelis chloris Slow worm Anguis fragilis
Green woodpecker Picus viridis Snipe Gallinago gallinago
Harvest mouse Micromys minutus Song thrush Turdus philomelos
Hedgehog Erinaceus europaeus Sparrowhawk Accipiter nisus
High brown fritillary Argynnis adippe Spotted flycatcher Muscicapa striata
Hobby Falco subbuteo Stag beetle Lucanus cervus
Hornet rove beetle Velleius dilatatus Starling Sturnus vulgaris
House sparrow Passer domesticus Striped lynchis moth Shargacucullia lychnitis
Jackdaw Corvus monedula Water vole Arvicola terrestris
Kestrel Falco tinnunculus White admiral Limenitis camilla
Kingfisher Alcedo atthis White-letter hairstreak Satyrium w-album
Magpie Pica pica White-clawed crayfish Austropotamobius pallipes
Meadow pipit Anthus pratensis Wood lark Lullula arborea
Natterer’s bat Myotis nattereri Woodpigeon Columba palumbus
Nightjar Caprimulgus europaeus
Noctule Nyctalus noctula
Northern lapwing Vanellus vanellus
Nuthatch Sitta europaea
Oak jewel beetle Agrilus biguttatus
Otter Lutra lutra
Palmate newt Triturus helveticus
Pheasant Phasianus colchicus
EXTENDED PHASE 1 HABITAT SURVEY 38 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 39 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
15 or fewer 10km squares in the UK (categories 1 and 2 of APPENDIX II: DEFINING ECOLOGICAL VALUES the UK BAP). Also sites supporting a breeding population Source: Institute of Ecology and Environmental Management of such a species or supplying a critical element of their 1. The examples contained in the table below are only for general guidance and other habitat requirements considerations may apply, e.g. features of low value in isolation but which are subject to Regional Sustainable areas of key habitat identified in the relevant cumulative national decline may be afforded higher values in certain circumstances. Regional BAP or smaller areas of such habitat that are Level of Ecological essential to maintain the viability of a larger whole Examples of Criteria Value Sustainable areas of key habitat identified as being of Regional Value in the appropriate Natural Areas profile International An internationally designated site or candidate site (SPA, pSPA, SAC, cSAC, Ramsar site, Biogenetic Reserve) A population of a species listed as being nationally scarce (i.e. occurring in 16 - 100 10km squares in the UK, or in a A sustainable area of a habitat listed in Annex I of the Regional BAP or relevant Natural Area on account of its Habitats Directive, or smaller areas of such habitat that regional rarity or localisation. Sites supporting a breeding are essential to maintain the viability of a larger whole population of such a species or supplying a critical element A sustainable population of an internationally important of their habitat requirements species, e.g. a UK Red Data Book species, species listed Sites, which exceed the County-level designations but fall under categories 1 or 2 of the UK BAP, or listed under short of SSSI selection guidelines, where these occur Annex IV of the Habitats Directive County/ Metropolitan Sites supporting a breeding population of internationally Semi-natural ancient woodland greater than 0.25 ha important species or supplying a critical element of their County/Metropolitan sites and other sites which meet the habitat requirements ecological selection criteria for designation
National A nationally designated site (SSSI, ASSI, NNR, MNR) or a A sustainable area of habitat identified in a county BAP discrete area that meets the selection criteria for national A population of a species that is listed in a designation (e.g. SSSI selection guidelines) county/metropolitan ‘red data book’ or BAP on account of A sustainable area of a priority habitat identified in the UK its regional rarity or localisation. Also sites supporting a BAP, or smaller areas of such habitat that are essential to breeding population of such a species or supplying a critical maintain the viability of a larger whole element of their habitat requirements
A sustainable population of a nationally important species or a site supporting such a species, i.e. a species listed on Schedules 5 and 8 of the W&CA (as amended) which is a UK Red Data Book species that is not listed as being of unfavourable conservation status in Europe, of uncertain conservation status or of global concern in the UK BAP
A non-Red Data Book species that is listed as occurring in
EXTENDED PHASE 1 HABITAT SURVEY 40 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 41 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
District Semi-natural ancient woodland smaller than 0.25 ha APPENDIX III: AN ECOLOGICAL EVALUATION
Sustainable areas of habitat identified in a sub-county The Criteria for Evaluation
(district/borough) BAP or in the relevant Natural Area 1. The criteria for evaluation have been adopted from the widely used set developed profile by Ratcliffe (1977). These were originally conceived to provide a systematic
Sites/features that are scarce within the district/borough or framework for the selection of Sites of Special Scientific Interest (SSSI) by the which appreciably enrich the district/borough habitat Nature Conservancy Council (NCC), but have since been adopted and adapted resource widely by ecologists, for example in Local Authorities and Wildlife Trusts.
A diverse and/or ecologically valuable hedgerow network The criteria used in this report are drawn from these widely applied criteria. They are: A population of a species that is listed in a district/borough BAP because of its rarity in the locality or in the relevant Size Natural Area profile because of its regional rarity or 2. In general, larger sites are more highly valued than smaller ones, all else being equal. localisation. Also sites supporting a breeding population of However, relative size to similar sites and other local sites should be considered. such a species or supplying a critical element of their The area of a site is also important in management terms, i.e. whether short-term requirements neglect/disturbance or any small changes would lead to the loss of a site’s interest.
Local Areas of habitat considered to appreciably enrich the Diversity
habitat resource within the context of the Parish or local 3. One of the most important site attributes is the variety of communities and species neighbourhood, e.g. isolated species-rich hedgerows which is largely dependent on diversity of habitat. Large numbers of species,
Site Small patches of poor semi-improved grassland, amenity particularly when represented by large populations, are to be valued. Diversity can grassland not used by Badgers also be related to habitat instability that may affect management prescriptions.
Negligible Areas of little current or potential ecological value Naturalness 4. Ecosystems least modified by man tend to be rated more highly. However, most
sites are influenced by man, the degree and nature of which is important.
Fragility
5. This reflects the degree of sensitivity of habitats, communities and species to environmental change. Fragile sites often represent ecosystems that are highly fragmented, dwindling or difficult to re-create.
Typicalness
6. The typical and commonplace within a field of ecological variation are also of value.
Recorded History
7. The existence of a scientific record of long-standing adds considerably to the value of a site.
EXTENDED PHASE 1 HABITAT SURVEY 42 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 43 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
Permanence APPENDIX IV: ASSESSMENT METHODOLOGIES, RESOURCES AND
LEGISLATION 8. A site that has been occupied by a semi-natural habitat for a long time is usually more valuable than one that has only recently arisen. This is because they have had Planning Policy Context and Legislation time to acquire rich assemblages of plants and animals. Planning Policy Statement 9 Lack of Modification 1. PPS9 Biodiversity and Geological Conservation (2005) sets out the Government’s vision 9. Adverse influences from humans, such as inappropriate management regimes and for conserving and enhancing biological diversity in England. It includes the broad pollution, will reduce the quality of an area. aim that planning, construction, development and regeneration should have minimal impacts on biodiversity and enhance it wherever possible. The broad objectives for Rarity planning include: 10. Rarity is concerned with communities and habitats as well as species. The presence of rare species adds to overall ecological value especially when a habitat also ranks Promotion of sustainable development highly on other criteria. The habitat type too may also be nationally or regionally To conserve, enhance and restore the diversity of England’s wildlife rare. To contribute to rural renewal and urban renaissance Position in an Ecological Unit Red Data Books 11. In the event of two sites being of equivalent intrinsic value, the close proximity of 2. Red Data Books and Nationally Scarce Lists (JNCC) classification of rarity is broken one site to a highly rated example of another type increases the value of the site. down into several categories, and these are summarised in Table 1 below: Table 1: The presence of other areas of semi-natural habitat adjacent or close to a site JNCC Classification of Red Data Book and Nationally Scarce Species enhances the value of both habitats.
Potential Value Category Status Definition 12. Certain sites could, through appropriate management or even natural change, eventually develop a nature conservation interest substantially greater than that Red Data Book 1 Endangered In danger of extinction, whose existing at present. survival is unlikely if the causal factors continue operating Intrinsic Appeal Red Data Book 2 Vulnerable Likely to move into the 13. While science may view all creatures as equal, pragmatism dictates that in nature Endangered category in the near conservation it is realistic to give more weight to the more popular appeal of some future if the causal factors species, groups or habitats than others. continue operating These criteria provide a useful basis against which to evaluate the intrinsic Red Data Book 3 Rare Taxa with small populations that ecological quality of a site, but in an urban area it is also important to consider the are not at present Endangered value of an area to the local people (GLC 1985). Thus the appeal of a site, its or Vulnerable, but are at risk educational and amenity value, as well as its accessibility as a wildlife area, need to be included in the evaluation.
14. The survey results were assessed and evaluated using these criteria as a guide.
EXTENDED PHASE 1 HABITAT SURVEY 44 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 45 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
derivatives, eggs, nests, etc as applicable) as well as damaging, destroying or Nationally Scarce Nationally Notable Uncommon taxa that have been disturbing nests in current use or dependent young. recorded in 16 – 100 10km squares in Great Britain. 6. Schedule 5 of The Wildlife and Countryside Act 1981 (and amendments) prohibits deliberate killing, injuring, taking, possessing, disturbing and selling (including parts The category is further divided and derivatives) as well as damaging, destroying or obstructing any structure or for some animal groups: place of refuge of listed fauna such as Dormouse, Otter and bat species. Nationally Scarce A: Recorded The Conservation (Natural Habitats &c.) (Amendment) Regulations from 16-30 10km squares. 2007 Nationally Scarce B: Recorded 7. The Conservation (Natural Habitats &c.) (Amendment) Regulations 2007, is from 31-100 10km squares. concerned with animal and plant species requiring strict protection. It is illegal to
kill, disturb, destroy eggs, breeding sites or resting places, pick, collect, take 3. Red List Bird Species are those, which are classified by the Royal Society for the cuttings, uproot or destroy in the wild as well as keep, transport, sell/exchange and Protection of Birds (RSPB 1996), as being of ‘high conservation concern’. Amber offer for sale/exchange species listed. List Species are those, which are classified by the RSPB (1996), as being of ‘medium The Countryside Rights of Way Act 2000 conservation concern’. Red List species have either experienced a decline in breeding population or range of 50% or more between 1971 and 1996; have 8. The Countryside Rights of Way Act 2000 increases protection given by The declined historically between 1800 and 1995; or are a species of ‘global Wildlife and Countryside Act 1981 (and amendments). The offence to intentionally conservation concern’. Amber List species have either experienced a decline in damage any structure or place that a wild animal listed in Schedule 5 of the Act breeding population or range of between 25 and 49% or more between 1971 and uses for shelter or protection or deliberately disturbing any such animal while in 1996; have a five year mean of between 0.2 and 300 breeding pairs in the UK; have such a structure or place is extended, so that the offence also covers reckless 20% or more of their European breeding population in the UK; have 20% or more damage or disturbance. The CroW Act also places a duty on Ministers and of the north-west European (wildfowl), East-Atlantic Flyway population (waders), Government Departments to have regard to the purpose of conserving biological or non-breeding populations (others) in the UK; have 50% or more of their UK diversity in accordance the Convention on Biological Diversity.
breeding or non-breeding populations in 10 or fewer sites in the UK; or are a The Natural Environment and Rural Communities Act 2006 species of ‘European Conservation Concern’. 9. The Natural Environment and Rural Communities Act (NERC, 2006) is designed to help Hedgerow Regulations 1997 achieve a rich and diverse natural environment and thriving rural communities 4. Under the Hedgerow Regulations 1997 hedgerows are important if they have been through modernised and simplified arrangements for delivering Government policy. in existence for thirty years or more and if they satisfy at least one of the ecological The Act implements key elements of the Government’s Rural Strategy published in or historical criteria as defined in the Regulations (Department of the Environment July 2004 (DEFRA 2006).
1997). The Protection of Badgers Act 1992
Wildlife and Countryside Act 1981 11. The Protection of Badgers Act 1992 makes it illegal to wilfully kill, injure or take 5. Schedule 1 Part 1 of The Wildlife and Countryside Act 1981 (and amendments) any Badger, or attempt to do so and it is an offence to intentionally or recklessly lists birds protected by special penalties at all times. It prohibits intentional damage, destroy or obstruct access to any part of a Badger sett
killing/injuring, taking, possessing, disturbing and selling (including parts and
EXTENDED PHASE 1 HABITAT SURVEY 46 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 47 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS ______ecosulis ltd ______ecosulis ltd _
APPENDIX V: LISTS OF BIRDS OF CONSERVATION CONCERN The wild bird species that are protected by special provisions at all times are listed (BAILLIE ET AL. 2002) AND LEGISLATION on Schedule 1, Part I, whereby ‘the intentional or reckless disturbance of… .whilst
nest building, at a nest containing eggs or young, or disturbing dependent juveniles’ 1. According to criteria established by the BTO, birds can be recognised as falling is an offence. into three categories, which describes the degree to which their populations are deemed to be threatened in the UK, namely the Red, Amber and Green Lists. Baillie et al. (2002) provides more detail, but the basis for defining these categories is described below. In addition, UK Biodiversity Action Plans (BAP) have been developed which set priorities for nationally and locally important species, each plan with actions to achieve the action plan target. There are 26 BAP bird species in the UK.
Red List Species 2. Red List species are those that are globally threatened according to IUCN criteria; those whose populations or range has declined or contracted rapidly in the last 25 years by 50% or more; and those that have declined historically (between 1800 and 1995) and not shown a substantial recent recovery.
Amber List Species 3. Amber List species are those with an unfavourable conservation status in Europe; those whose breeding population or range has declined or contracted moderately (25 – 49%) in recent years, or whose non-breeding populations have declined to a similar degree; those whose population has declined historically but made a substantial recent recovery; and those, which are rare breeders or have internationally important or localised populations, coded BR (five year mean of 1 – 300 breeding populations), BL (50% or more of UK breeding population in ten or fewer sites), WL (as for BL but relating to non-breeding populations), BI (20% or more of European breeding population occurring in the UK), or WI (20% or more of various other European or ‘East Atlantic Flyway’ populations occurring in the UK).
Green List Species 4. Species that fulfil none of the above criteria are green-listed.
Schedule 1 Species
5. The legislative provisions in Great Britain for the protection of wild birds are contained primarily in the Wildlife and Countryside Act, 1981, Sections 1-7. It is an offence to intentionally kill, injure or take any wild bird; take, damage or destroy a nest (whilst in use or under construction); take, damage or destroy its eggs; possess wild birds (dead or alive) or their eggs.
EXTENDED PHASE 1 HABITAT SURVEY 48 DTZCON-PINSTU-1480 EXTENDED PHASE 1 HABITAT SURVEY 49 DTZCON-PINSTU-1480 PINEWOOD STUDIOS PINEWOOD STUDIOS
! " # ! $ $ $
%&' ( ) *% +, -++. / 01&1%2&%'3-++. / 002 22&% " " 4$ $ 0 +
@ % 83 % '@ 0# ' ! # % "% @ % " @ ?= 3 % "& < 9$A % "+ % & @ &"% : &" @ &"& @ &"+ &"2 < &"1 + < & +"% : & +" B$ & +"& @ & +"+ 2 +"2 < % 2 < % 2"% < % 2" %& $%< ! ! $ " $: !$ @ C $& $+ !$ @ @$ $2 $ ! !$ $1 ! 8 @ < '@ %8@' '@ '@ & < '@ + < R ' C '@ 2 < R ' %1 4 C '@ 1 ! @ R '
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= 9< ? # %%
!@!! !)! ! ) ! ) ) ! )$ " %"%"%"% <$ ! ) A ) $< $ < !$ ! $ @ " 4 C" ! %B$ $ ! ! @@ ! " "%"%"& @ '@ % $! ! ! ! @ ) ! ! " %"%"%" ! ) $@E $ + ! " !"
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
$ "# ! !! $ "&"%"% $A ! !@! 5 @ !@@ $ ! ! @ "' !! $ $ $ $": @ ) $ ! ) @ 3 @$ ! G @ $ ! " $ !$ G
%"%"%"0 @ $ " ! $ !!@@ @ R ' $ G ! E!@! ! $ 3 !$ G ! @ G! @!@ @ $ G !$ $3 G @ $! @ !@@$ " ! .!/ 3 !$ G %"%"%"C # !! $ @ . 3 0"2 % / $ " ! ! @ ! ! ! @! @ G
! @ "
"%"%"% < $ )< C) ! ' () @ !+0"& A .3 @ ! "+"%"% '@ # ) @ , %C++/"9! ! $ ! " & ! ! $ ! " ! %B$ $ " + ! @ ! C.8 /" @ @ $ $! "%"%" !@E! @ ) $ @ $ ) $ " $ #B "# !@! ) @3 !! @) ) ) @ E
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @% 9< ? # %% # *+ # , @@ !! ! $ ) $" ! &"%"%"% < ! 83 %B$ $8 !! 3 C" + ! $ @ $ "$$ ! @ @ " H 8 = "7 8@ 8 <@ E ! $ $ ! " $ @$ " )! ) $ ! 3 " # ) B@ @ ! @ )@ &""%"% < %2 < C$ ! $ @ ) " @ ! !! $ $ @) @ !@@$ " !@@ " !5
$ @ A $ $ @$ G &"+"%"+ 8 @ ! @ @$ % C %% C) $ ! < @$" $ ) ! $ $ @$ G # - $
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
# .
&"1"%"% @ A @ !3 $ @ ! I$ !$ "# $ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @ 9< ? # %% ) @E ! $$ @ $ +"&"%"& . E $ !" $ @@ ! @$ @ " !! !! ! ! @ $ ! @$ $ @@!" ! !! ."@" )$ /"# ! ! $ "9 $ " $ $@ $ )$ $ @ " +"&"%"+ < ! " ! @) ! ! ) $ ! $ @. / @ !"< @!$$ " $E@E $ @ $ @ @ &"1"%" 3 )@ ! < ! ! "< @$@E $ @ 4 "< @ !$ ) @$ " @ $ @ $ )! ! @! !$ @$ @$ 3 $ !$ E ! @ " " ' ( $))
' ,
+"%"%"% $& $ " () * +, & + - &
7 & %"0 E !
= 1 %"0 E !
@E $ % "& E !
' /
+""%"% !@$ $ @)!@@ @ !$ "
' 0
+"""% *% * .!!E /5 $ ) +"&"%"2 ).@@ @ !" @ $!@@$ !$ @$ " @ @ $ @ $ @ !$ @$ ) @$ " $ @"
+""" * = 5 $$)$) @ !@@ !$ " @$ . $ @ /"* @ $$ $ $"< E @@ $ ! @ !$ "
' # +""&"% %.!!E /5 $ $ $!@@$ !$ @$ "
' ' / 1 +""+"% A ! @ $ @ !@@ !$ ) = " @ @ $ $ ) " ! @ @ $@ .! $ $/) @ !@@ " B @ B+ B1 ! $) E $ E. @ /"
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
+"&"%"% +5= ! $($ @ ! $ ! "9 ! @@$ ! $ @ $ $ @$ $ ! 3 "
+"&"%"C . @$ @ @ ! ! ! " @ $ )$ ) $$$ "7 @ !$ ! $ @ @$ $ !@@ "
+"&"%" 1.* @ ! $ @"7 @ ! @ $ ! @ $ @ $ @ @ ! @ "9 @$ "
' # %332 +"&""% ).! !"< A $ @ ! "B@ $ $ @$ "
+"&"" ) .@ $ .' 8 ' / ! ! @! @@ ! !$ @"< A @ !@@$ "B@ !$ " A $ @ $ ! ) @$ "# $ $ @ ! $. @ ! /" 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @+ 9< ? # %% +"&""& )3. @ ! "< A $ ! +"+"%" %5 $ )& @ ! @ ! "B@ @$ $ ! ! @ !3 2 "7 $! "83 $ A !!@@" $! $"B@ @$ $ ! !$ *%. * /!!@@" +"&""+ )4.@$$E @.* ' / ! @ @$ "
+"&""2 )5.@ $ .B ' /! !@ " @$ " $ @ @ ! $"
+"&""1 )#.! ! ) @ $@ " @ @$ "
' # # +"&"&"% $+ '@ 1 0 ! !$ @ $ $ @ $ " - ! ! )!
&
< =! $@E =! $@E @ M! @ +"+"%"& 5' !! ! ! R ' "83 $ = & @ "7@@$ : @$ "
8 +"+"%"+ &5@ @!. @ @ ) $ /"< 3! @$ ' E @ $ $ ) $"' $! F =! $@E @ M! @ "83 $ @ @ $ "B@ @$ " + 7@@$
% B@
B@. $ @ /
2 B@
1 B@
0
C E@
' '
+"+"%"% @ ! %0 ! @$ " ! '@ $ @ $"# $ ! $ $ !@ ! $@ $ $ " = ) "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @2 9< ? # %% +"+"%"1 25 E $ @ !& "= 3 % ) @ @ $ " @$ "
+"+"%"0 15@ $ !@ " $ $ @ !3 "=$$ ! +"+"%"2 +5 @ "7 $! "83 $! $$ " $ @ $ $ E$ @ $! " 3 ! $ @ "9$ $ @$ " 3 @ )$ 3 ! $ "9 @$ $ ! $ "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @1 9< ? # %% +"+"%"C 05 @ @ !0 "7 $! "83 +"+"%"% 5 E @! ! $ @ ! $ ! @ @ " &"2 " $ $ @ 3 @@ " @$ " !! & "< 3 C " ! 3 $ ) @ @! G) !! @ ! = ) @ !@@$ "B@ @$ "
+"+"%" C5 " ! 2 @ % "7 $! "83 $ ! $ @ @ "B) ! @ !@@$ $ ! @ @$ "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @0 9< ? # %% +"+"%"%% % 5 @ $ @ !C +"+"%"% %%5 $ @ !3 &"2 ) $ @ "B) @ ! ! $ ! ! $3 @ $ @ ! " ! @$ " $ @ "7 $! "83 $ ! @ ! $$ "9 @$ "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @C 9< ? # %% +"+"%"%& %5 $ @ !+ $ @ +"+"%"%+ %&5@ @ $ @ !%2 "7 $! " ))3 ) @ !$ ! " $ !@ ! " $ ) @$ @ @ $ @$ " $ " @ @ !@@$ $ @ ) ! @$ "
+"+"%"%2 %+5@ @! @ !C 3 @ " ! $ $ 3 ) @ @ "7 $! "83 $ ! $ @ !$ " @$ "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @ 9< ? # %% +"+"%"%1 %25& @ . $/ 3 @ 3 % ) +"+"%"%C %059E ! @$ "A !$ @$ ! " @! ! " @$"=@! $$ @! "7 $$ " 83 @ !$ ! " @$ " @$ "
' ' 3 +"+""% < $) ! ! ! $$ "< @ @ ! @ @ $ . %) &) C / $ $ @@! ! "B) ! $! $ ! $ $! $ "' ! !$ ) ! "
+"+"" < ! $2 '@ 0" 3 +"+"%"%0 %15# @! ! 3 @ $ $ @ "! @ !3 "83 ! + !$ " @$ " 7@@$ %
+) % ) %%) %2 +
E 2) 1) 0) %&) %+ 2
%) %1) %0 &
B@ %) &) C) +
' - $
+"2"%"% ! $ @ $1" ! E $ '@ & @ R ' '@ + 2"
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @% 9< ? # %% 4* ) 1! ! ! %" " = @ B @7* * "2 .$$/ @$ @ E !! 'C. .
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
&"%1 = < A B ' . @0/ B 2"%""& R ' " !) &"% = '@@@ @ $! R ' $@E $ $ !! $ "B) ! !! $ ) $ &"1 7 B $! A R ' $ @ . !! !@ @/"# @ &"C @E B $!.& / A R ' $ @ @ !@@ $ &" = '@@ B A B ' . @0/ ! "=@ @@ ! $ @ $! $$ "< @ ) $ $) $ &"&1 = $ @ !@@!@ ! = 2 "
&"+2 '@@ @ @ @B%& 2"%""+ 9$ ! $$ ! ! = " = $ 9 $ ! G ! $ !! " &"2 '@@= %2 !! @ @ E . !!@@$ / $! ! " $! &"21 = '@@ @BC = $"
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
- ( 2""2"& $ @ @B $ ) $ !!( $ $ A 2 "<$ ! $ @ 2""%"% < $ $)! $ $ !! ! "B) @ @ $$ ) $ !! '% ' $! !@@$@E $ ! 8 .8 / $ !"7 8@ @ $ ! $! " $ ! $ ! @ . / $! $ )!3 $ $!$ " @ ! "
2""%" @ ! R ' ! - . * $ ! $ " 2""1"% # A @ @ !2 ) $ E @ !$ 0"2 % ) @ $ - @"# !! $ 2"""% A ! ! @$ @ $ "<! !! $ @ ) " ! @ ! @ $ $ @$ $! $ ! $ " $ $ ! @ !@"# ! @ $ $ ) $ @$ $ ! ! "#! !$ ! $ ! E! $! @ @ @ $ @ "= $
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= @%& 9< ? # %%
%627*1
%!1! % %! ) %!() * %!-) R% 8 ""# %!3) R% 4 &9 ""# %!4 )! R% ) * %!56 % )
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "< ":9= 9< ? # %% '- / !! ) '* , " ,- ++ +2&)2&3 45 4 " " 01 -- +* & !"# &$!!%&'(&)**+ , -,. 0 +0 ((& 1, * , 0 . /!!! * !! ( Pinewood
! !! '
' ' '
! ! !!
' " # $ %
!!!
'
'
!!!!
'
' ! '
' ! !!
'
'
! !!
" & "
'
'
& ,2 2 +, 30 ! !!
!! !!! !! !! !! !! ! !! ! !! ! !! ! !! ! !! ! !! ! !! !!!! ! !! !!! ! !! ! !! !!! ! !! !!! !!!
!! +* & & # !! # & & & & " # !!! ( - (&&3 & / (&&3 !! 0/ (&&3
(( / !! # +0 (&&3
*0 (&&3 !! (+0 (&&3 # !
(32&)2&3 45 4 " !! # # " 01 --
# / !! # &3),+ )+ +& # # # # !! # # !"# $!!%&'(&)**+ # , -,. !! # & 0 +0
!! Pinewood
&0 4 +,0 !!
! ./!!!
!!! *
!! ( !! )
!! '- ! !! ! !! !!!! !!! ! !! ! !! +* 7 - .. !!! 0 5 .. 7 - .. 8 * / 9 7 - 9 9 " 2: 9 !! . .- .8 -
!
(32&)2&3 45 4 " " 01 -- !! / &+& && (&& !"# $!!%&'(&)**+ , -,. !! 0 +0
Pinewood
&0 ,0 04 4 0 !!
. /!!!
*
!! ( !! ) '- ! !! +* 7 -
; < 8 "
"
B
B
B B
B
B BBBBBBBB
4 B : B
B B
B
B
B
B
.
B .B
B B
B B
B
B B B
B
B
B B
B B
- +2&)2&3 45 4 "
B 7 B
B - B
" - B B " 01 --
B
B
/
B B
&3*!
.
B
: B
B
B
-
B - B
B B
-
7 B B
B B
.
:
B B
!"#
$!!%&'(&)**+ B B
, -,.
B B
B B
B B 0 +0
B B 8
B
B
B B Pinewood
B
B
B B
B
. B &0 ,0 04 0
. B B 4 !! ! . ! !!! * !! ( !! ) '- ! !! +*
7 -
< 8 " ;
"
B
B
B
. B BBBBBBBB
. 4 B
B
7 B - B
:
B B
B B
B B
B B
B B
B
- B
B 7 B
B
B
B
:. B
B B
B
B
8 +2&)2&3 45 4 " B
B
B
" B
B B " 01 --
B
B /
B
B &3*!
B B
B
B
7 - B B
B B
B
B
B
B
B B !"#
$!!%&'(&)**+
B
B , -,. B
B B
B
B B 0 +0 B
B B B
B
B Pinewood
B
B
B
B
B B &0 ,0 04 0
B B 0 6 !! ! . ! !!! * !! ( !! ) '-
" 9
" 2 # 9
B
B
B B
B
B :0# 7
B B
B B
B B BBBBBBBB 6#
B B
B B
B
B
B B
B
B B B
B B
B B B
B *15(+5(1 67$ 6 B B
B
B
B B ! 34# //#
B
B 2
B
B (1 ,
B B
B B
B B
B B
B
B
B
B !
B B " # $ %
& '()*( +, , -
B
B ./. 0 B
B B
B
B B ! B
B B B
B
B Pinewood
B
B
B
B
B B "
B B # " ' / 501400 501600 501800 502000 502200 502400
B5 Legend Suspected B2 Site Area Pipistrelle T1 Roost Commuting/Foraging T2 Trees with Bat Roost Potential B1 B3 B6 Negligible B7 Low
185000 T3 Low to Moderate
Moderate
B4 Moderate to High
High
Confirmed Buildings with Bat Roost Potential
Negligible 184800 Low T4 Low to Moderate
Moderate
Moderate to High High Confirmed T10 D1 21-07-08 HRW NH NH 184600 Issue Date By Chkd Appd T9 Metres T11 Suspected 050 100 200 Noctule T8 Roost
T12 T5 13 Fitzroy Street T13 London W1T 4BQ T14 T15 Tel +44 0(20) 7636 1531 www.arup.com
Client 184400
T16 T17 Pinewood Studios Ltd
Job Title T6 Pinewood T7
B8 Suspected Drawing Title Pipistrelle Important Features for Bats Roost 184200
Scale at A3 1:4,000
Drawing Status Figure 7
Job No Drawing No Issue 207042-18 008 D1 oFileLocation © Arup
! "
F = 7
F = 7 <
! " # ! $ $ $
%&' ( ) *% +, -++. / 01&1%2&%'3-++. / 002 &2% " " 4$ $ 0 +
F = 7 @ @ % 83 % # % "% @ % " @ ?= 3 % "& < 9$A % "+ % & @ % &"% : % &" @ % &"& % &"+ + < +"% : +" @ +"& 2 = & $% $* = @ $& '@ %8@' 5
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "&F=7":9= 9< ? # %<
F = 7 $ I$ !@ G %"%"%"% <@ ! ) A ) $< @< C" ! %B$ ! ! @ ! ! $ ! ! @@ ! " ! @! @ G %"%"%" @ $ %" E ! "< .: $ 0/! ! @ " @ A ! " ' ()
%"%"%"& $ !@ ) '@ ) @ @ ! @$ @)@@ ) @) @ ! @ "+"%"% ! " & ! " + " " %"%"%"+ 7@ ! @ " # *+ %"%"%"2 !$ @ ! % !$ @!@ " $ @ # , "#! $ @ ! ) ) !$ ) ! $ &"%"%"% < ! 83 %B$ $8 @ ! $ " C"F ! $ @ H 8 = "7 8@ 8 <@ $ ! "
# )
"%"%"% < $ )< C) ! &""%"% 7 8@ @ $ $! @@ @ !+0"& A .3 @ ! , 2 ! ! $ ! @" $ %C++/"9! ! @ $ !@ ! ! !@ ) @ ! ! " ! @$ @ ) @ @ ! %B$ ! C.8 /" $ @ ! $ $ "< ! 9 @ ! $ 2 ! " "%"%" !@! @ ) $ @ $ ) $ #B "# !@! ) &""%" <! $ 3 ! %2 < C) @3 !! @) ) ) @ E 3 $ ! $$ @ $ !@!! !)! ! ) ! ) $ $ !!@@ $ " ) ! )$ " # # !$ ! $ @ " !@ ) ! ! !! !" &"&"%"% "F ! @@ 8@ 7 .
""%"% @ 8 ;H * !?= 7 8@ /F = 7 @ F . %/) B ! *R < % C% = .7 B$ ?/@ % +"# @ $ ) .% C/" 5 A ) $@ $ $ " )) $ @ @ " @ ! @ @@@ ) )A " &"&"%" $ ! ! @ @ $ . $2 =/"7 8@ ! !% !$" ""%" F ;H < .</"F $ $ A " ! !;H@) ! $@ @ $ @! ! @@ +
"; 7 8 = .78=/< 1) &"&"%"& ! @ ! !$ @" !@ < ! $ @ @ . /! @@ I $ "F) !@@ !@ " $ ) "
# $ % & +
&"&"%"+ < !2 ) $ ! " "&"%"% $A ! !@! 5 !! " @ 3 @@ ! @ G @) @ " @ " !! $ $@ G
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "&F=7":9= @% 9< ? # %< F = 7 5 ) $!@@$ " @ ) !@@ " &"&"%"2 7 8@ !! !%2 @2 !$ @
E+ " !! )$ " +""%"& . A !! )3 % ! $ ) .% 3%"2 / (3 + . / " @ ! 3@ " @ ) ! @ @ &"&"%"1 7 !! @$ ! ! $ "< !! @ " @$ $ $ ! ) @ ) $ )!@! $$ @"7 ! @ @ !! @ $ ) @ @ ) $ )$) ) I " @ $$ " ! !@ 2
&"&"%"0 7 8@ ! $"' " @ ) !@ ! ) $ )$ E E4 ) @@E@ 3@ " $ E" $ E< E"#!@ ! @ +""%"+ (. .2 3% / .2 / ! @ @ ) !! $3 3 " @$ @ @( $$$ $" ( " 2 @ 3
&"&"%"C < @ $ ! ) $ ) $(" @ ) %" ! @ A ) @ @ ! @@ !@@E@" "2 !!@! $$ " $ E"
8 & & +""%"2 -. .& 3& / .N / ) @@ ) 1!! & + ! *! " ! @ ! $! $ ! & & @ !! "
% .% / +""%"1 &.< .N% ! / @@ $ "7 $ @ ! ! "
& ' %3320 61+-778 +"""% <@ @ ! )3 +2 # ' E ! "< ! = ) 3 + ! " . @ F &"+"%"% < ! @ ! @ ! ! / $ ! $ ! F) ! "# $ $ ": ! $!@@$ @ !!E $ ! @ !! $ "#! ) $ $ @@ $ " !!@@"B)@ $ $ @ !! @ ! ' ! ) @ ' # ( " +"&"%"% $! @ ) $" ' ( $)) ' &0 ! & ' , ' & + :0; 0 ' * +"%"%"% @ $ %" E ! ": @ 83 %B$ $8 % &E+ < C %% = % K @ $( : C) $ %"<@ A @ C$= < %" % E C % = 2K : ! @ A @&"&" & %%E% C %2 = ( :
' ) + E& C %2 = ( :
' %20
+""%"% ! $ '@ %" +"&"%" $&"7@ ! @ " !$ @ ! % +""%" . 3 ) @3 % 3%"2 & " @ )$ $ $ " @$ !$ @!@ " $ @ @$ @ ) @ "7 $ &"
%= .4 C/ @&"&F 5 " 5 "!" " 0I & 2I " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "&F=7":9= @ 9< ? # %< F = 7 ( *
8 & + & + 1!! &
% %V )%!@ E
& %V %@ V %W 0!@
+ %@ V %@ V W E -!@
% E
E
&?+ M
(
% E
E
&?+ M
+"&"%"& 7 $ @ !! @ $$ ! " -
2"%"%"% ! @ " ! "
2"%"%" < $! $ ! @ %"#! $ @ ! ) ) !$ ) ! $ @ ! $ "
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "&F=7":9= @& 9< ? # %<
%627*1
F = 7 %!1! % .
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "&F=7":9= 9< ? :! %%% '- / !! ) '* , " ,- ++ +2&)2&3 45 4 " " 01 -- +* & !"# &$!!%&'(&)**+ , -,. 0 +0 ((& 1, * , 0 . /!!! * !! ( Pinewood
! !! '
' ' '
! ! !!
' " # $ %
!!!
'
'
!!!!
'
' ! '
' ! !!
'
'
! !!
" & "
'
'
& ,2 2 +, 30 ! !!
!! !!! !! !! !! !!
# $% &
@ :
@ : <
! " # ! $ $ $
%&' ( ) *% +, -++. / 01&1%2&%'3-++. / 002 22&% " " 4$ $ 0 +
@ : @ % # % %"% @ % %" @ ?= 3 % %"& < 9$A % %"+ % @ % "% : % " @ % "& % "+ & < &"% : &" @ &"& & &"+ < + + = + ! '@ %8@' '@ @ = @<
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "+<:F8:99; 8":9= 9< ? # %<
@ : ' ()
%"+"%"% '@ # ) @ ! " & ! ! ! @ " %"%"%"% < $ )< C) ! + " @ !+1 A .3 @ ! , % %"+"%" @ '@ % $! ! !$ C++/" ! ! @ $ @ ! ! " ! .@ ! @ ! /" *+ ! %B$ ! C.8 /" , %"%"%" !@E! @ ) $ @ $ )
$ #B "# !@! ) "%"%"% < !83 %B$ $ @3 !! @) ) ) @ E 8 C" ! ! $ !@!! !)! ! ) ! ) @ H 8 = .;=H H8=/" ) ! )$ " !$ ! $ @ " "%"%" 9 !$ ) @ 7 7 .77/$ ! ! $ " !" ) %""%"% !@ ! $ @ " ""%"% ' ! )! $ 3 @ %2< C" @ !! $ %"""% @ ! @ < )% " $ @ "# ) !9 @ ! !!E ! 3 "'@! %""" = ) !! 5 ) !@ @ )A $ @) G "&"
! $ @ $./ @@ !G.$/ @ G./ # $ @ ! G. / @ @ G./ $@ $ @ @ " # @ )! @ $$ ! $ $ # , "&"%"% $ @ " ! )! $ ! $) %""&"% : 8 ) ) $ )A @ " $ ) ) 3 " $ = .7 B$ )?"/@ % +)= @ !*.=*/< "&"%" !@ !$ @ ! @ 5 * ! = < % C%. /" $ @ G %""&" : ;H < .</" !) $ @ G !;H@) ! $@ @ I G $ @! @@ "; 7 ! .@ ) @ )!@ !$ @ 8 = .78=/< 1) !@ /" < ! @ " "&"%"& <) ! @$ @ " ! $ @ <. /)@ @ !@ # $ % & " $! @ ! @
%"&"%"% $A ! !@! 5 ": @<) $ @@! ! ! ) @ ! " @ 3 @$ @ ! G # , !! $ $$ @ G "&""% @@ Q !"#$ I$ !$ @ G % R.8@ 7 ) 1/"
! ! @ ! ! "&"" $$ @ ! ! " ! @! @ $ ) ( "< G $ ! $3 $ ! ) " 7 $ 3 @ @ $7 ! @ " "&""& 8@ .! 8@ 7 /"
456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "+<:F8:99; 8":9= @% 9< ? # %< @ : "&""+ @ !% 3% ! ) @( # , ! ! " $! (! &"""% ) $ @$ ! .@@$)) @@! " @/ ! () ) ) ! $ " ! A @ $ ! "&""2 $ $3 $ 3 @ + < " $ $5 C"< ! $ 2 $3 ) $ $ ! 5 '
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inewood ! !! ' ' ' ' ! ! !! ' " # $ % !!! ' ' !!!! ' ' ! ' ' ! !! ' ' ! !! " & " ' ' & ,2 2 +, 30 ! !! !! !!! !! !! !! !! ! +* &* , 0 /!& ..&3 '- 0 8. )22&3 45 4 " 0 .5 " 01 -- Pinewood / &(! A&3 /(+ !"# $!!(&)**+ =$!!(&)+3&>(! , -,. 0 +0 Pinewood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inewood ! !! ' ' ' ' ! ! !! ' " # $ % !!! ' ' !!!! ' ' ! ' ' ! !! ' ' ! !! " & " ' ' & ,2 2 +, 30 ! !! !! !!! !! !! !! !! ! % ! "# $ " !% 07,.7,8 9' ! % 56 22 4! ,.0 0, ,, !$% !! & '#( # )*+,-,.//0 1 21"3 ! '" ! #! #! (! ) &! "# $ * + " ! %& !! &"! ' 2 ! !! ! !! ! !! !!!! !!! ! !! ! !! !! +* " & " ' * 04 4 07 4 4 07 ' + 04 7 4 !!! ' 7 4 ' ' ' !! ' +2&)2&3 45 4 " " 01 -- / &++ & ((& !! ' " # $ % ' ' !"# $!!%&'(&)**+ , -,. ' ! 0 +0 ' !! Pinewood ' ! ' ' %0 04 ' !! . /!!! * !! ( !! ) '- =2* = & ! &.%% ! & & ! &(.%%C&,! & &!,= = B @B% & ! &-.%%#&,! & &!,=# & ! & .%%"&,!&!,=- =3 = B @ BC B @ B%+ B @ & ! &3.%%5 ! & & B%2 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "28 #8 ":9= 9< ? # %< < 3< $ 0 +, 8 *#7:5 =9;: 5 .=/ . ) . / .) @ ) @ ) ) ) @/ / : M [ [ CE<E C % % %1 @ 2 7 %1 @ 1 %EE % % @ C @ C % @ C @ CEE & % C +E2 @ %1EE + % % @ C C CEE 2 % %2 @ C C E4 E C 1 % %2 @ C % @ 0 % E4 E C 0 % %C @ + %1E4 E C C % % 1 CE4 % 2 %2E4 E C % % %C @ C 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "28 #8 ":9= @<% 9< ? :! %% $ ( 1, 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "28 #8 ":9= @<% 9< ? :! %% 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "28 #8 ":9= @< 9< ? :! %% 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "28 #8 ":9= @<& 9< ? :! %% ) & @ @ < ! " # ! $ $ $ %&' ( ) *% +, -++. / 01&1%2&%'3-++. / 002 22&% " " 4$ $ 0 + @ @ @ % 83 % # % "% @ % " @ 8@ @ % "& < 9$A % "+ % & @ % &"% = % &" ' % &"& + < +"% = +" ' +"& < ! @ & 2 = + 2"% !' @ + 2" @ = + $%7 $ ! = $ @ $&H @ '@ % H< !< '@ H %!+.H / '@ &H !+.* $ / '@ +H &!+.F *$ F / '@ 2H +!+. @ !/ $)) < 3< ! < 4 C < 3 <$ = 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= 9< ? # %< @ @ ) $@ @ " %"%"%"% <$ @$ ! A ) A ) $< ! < C" ! %B$ $ ""%" < $ ;H $ * ! = < % C% ! ! @@ ! " . /" !! $ A $ ) @ )@@ @" %"%"%" < ! $3 @ $ < 4 $ ) @ @! ! ""%"& = !! %! < ! " ! ! R !! $ $ $ ) $ @$ " @! @ ! " ""%"+ ! @ ! @ %"%"%"& < !2&$ @ G+ ! @ "7 $ @ $ @ ( ! $ $ ! $ ) @ $! $ % ": $@ " $ ! @ !! @ !! @$ @! ) $ @ "H . +/" $$) ) ) ) @ ) @) ) # $ % & $ !" ! $ @$ $ ) $ ) (" ! 5 %"%"%"+ H ! !$ @$ = ) @ $ $ !$ @$ G ! = ) ! ! $ @! " ! $ ! ! $ @$ !$ ! = @ .3 ! ! G $A !! @ /)$ ! A ! $ @ " ! @! ! @ $ ! $ @$ G %"%"%"2 # @ ! $ @$ ) $! @ $ " ! @ $ @$ $ @. @ $ @! @ / $ !! " ) @!@! $3 $ ) ' () @ ) @!@ $ @ ! @ ) @ "+"%"% '@ ) @! @ @ @$!" ! " & $ ! ! $ @$ ! " + ! "') 2 ! @ " "+"%" < 3% ! ! $ @ " "%"%"% < $ )< C) ! "+"%"& '@ % !$ @$ @ @ !+ A .3 @ ! , "'@ 2 ! @$ " %C++/"9! ! $ @$ ! " ! %B$ # *+ ! C.8 /" # "%"%" !@E! @ ) $ @ $ ) $ #B "# !@! ) &"%"%"% < !3 @ !$ @$ $ ! @3 !! @) ) ) @ E @ @ H 8 = !@!! !)! ! ) ! ) .;=H H8=/) ! %B$ .8 ) 0/"< ) ! )$ " ! " !$ ! $ @ " &"%"%" ' $E$ ! ! $ ! %) @ 7 7 .77/" # ""%"% ! ! $ @ $ @ ) @ @! )$ &""%"% < !!! $3 @ @ @ E "< @ @ $ $ @ ! 4 C" @ $ ! $ @ @ 4 ) $ $ ! ) $ ! .<)4 /" @$ @ .!3 $/" @$ ! @ ) @$ $ " $ @ $ @ @ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @% 9< ? # %< @ % &""%" @ ."@"$$ ") F$ ")% C / ! + 0 * ! " @ ! = = ) $ $" H@! & %"2 *! * % .% ! )77/ &""%"& < ! )$@ ! E ) @ ' % "+ 7! !! " )$ : ! *$ % % *! $E " = $ % % *! $ !! ! !! $@ " &""%"+ 8 3 + @ @" +"%"%" ! .$$) ) ! $) $/ ! $ 0"& %%"& )! ! @ $ ! $ "<! !$ E ! " ) ) " ' &""%"2 9 )$ A $ ! ) @ !9 @. 9/ ' ,) "' @ @ 3!$ $ ) + ! !! $ )$ $ E $" +""%"% @ ) @ ) $ " ! @ &""%"1 $$ @ ! !@$ $ 5 ! = @ $ $! ! "< ! @$ ! " @@@ ! G +""%" 9! $ ) ! $ @$ )$ ) @) E@) ! ! $ G = !@ " @ ! .! ! / G ' ( @! @@$ " +"""% < !2& !$ A $ < 4 C"9! ) + $$ @ ) ! 5 &""%"0 * $ @$ ! )$ ! $ $ )A @ ! $ @ $ )!) ! 3 3 @ ! " H * 4 &""%"C @ $$ @ E!@ ) B$$ * 4 $$ ! @ @ 3 " *@ * *$ == &""%" ; ! 3 ) ! $@ ! @ ! '@ * =!!!! @ ) $ ! ! * @ : F B ! ( " = : $ F =!! # # 9 @ &"&"%"% 7 $ ! $ ! F* $ @E F ! ) I@ @ " F * F *$ 7 F! ! " @ ! ' ( $)) ' +""" ' ! $ ! ! < 3%" $ !$ $ '@ 2" +"%"%"% !@ !$ $;=H H8=. I 77$ /! ! ! " +"""& !@ ! ! @ ! " + )*0 9* 77; + 0 * +"""+ = ) @ G % := @ %&:=$ ! " B$$ & % *! +"""2 F $ ! $ ) )$)$ @ )! @ % "& 8! " @ $ ) @ $) = % *! $) ) ) $ !!!!"<$ ! @ = @$$ ! )! ! ) = ) A #B @" %$$)="4") . / = ) 8 E< F$ )F")F$$ ):)*" 8 )4".% C/ @ 5< ! !H;H M 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @ 9< ? # %< @ 9.* 77; @ ) @) ! $ .47==+ $ /" +"""1 = %:=" +"&"" @ ! @ H +"""0 ! ! ! ) @ @ 2 $ "*$ $ $ ! < .</) I @ ;H<) ) !!!!" @ $ 3 2 ) ! ! @ ! ! ! ! . ! ! = ) $! @@!! $ "<$$ H 8 = M8 = )4 1 @ @! = @ E ! " C /" ( D )!) #9;* 77; ' 0 +1*0 7D) +"""C = ) $ G ) %2:=" +""" ! ! 5 @ "< @ H .%/ < $ $ @ . ! A B$$.%/ % $/) $ ! R ' .$ / ! ! "<$$ !@ ! F* .%/ < $ ! #B @) ! @ = ) @ .%/ # ! = " ./ < $ '97<77; .%/ < $ +"""% = E %2:=" : .%1/ # < $ +"""%% * $ ! ! ! @ ! ) $ ! @@ $@ G $ @@@ ! @ @ @ .C/ # @@ " $ ! R ' ! * *$.% / < $ @ %+ ) @% @ ! " $$ " F .%/ < $ -9-<77; @.%2/ # +"""% = $@ )$ @ ) $(G B .2/ # % := @ &:=$ ! " .2/ # +"""%& '@ !@ ! ! " @ @ ! @ R ' ! "<$$ @ ) !./ # @$ @. 8! / = " ! .8 / @ = " $ ! @@$ +"&""& 7! $ E.N% ;H/G ) ! ) $3 !" ) !$$$ @ ;H. ) 10/) @ $ $ % " ;H$ @ ! % ) ) !2)C " +"""%+ 9 ! ! @ !@ @<" +"&""+ 7! $$ @$ ! ! +"""%2 #)$ (( $ !@@$ ) ! = @ @! ! ! = " <" +"&""2 !! @ ) $ +"""%1 #4 ) 3 @ @ !@ $!@E " !!@ )$ ! $ $ ! !$ 3 E " ' # $)) 3 ' # # , +"&"%"% @! @ $ ! "F) )(+ $ ! $ ! ) . / ( ! ) ! $' .% C /&" +"&"&"% ; @ ' @) !+ !$ @$ $@ $ @QR! .2E+ /) $ ' # ( " +"&""% 9! $ $! $ @ ) $ $ $ !! .!3 ) %! @ ) + ( !# > ( / ! ) 47==. / ! ;H5 != = E 0 2 @ H . 0/ @ H < E % 1 @ H 8 = M8 = .4 C/ = ! !* ! ) @ 93! .M ):! / 0)B") ):"<")<$ )7"<")= )"<")F@)":") )="<")7$):"F") ! )"". 1/ &' )4.% C /< !< @ 9 @# ! != E !9 @ 8 ! F ; H@ E )4 1)2E++ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @& 9< ? # %< @ ! "' $" +"&"&" * $$ @ . < 3/) ! A ! ! .% / C " - * ) * +"&"&"& * ! ! !! @ ! ! @ $ @ @! $@!$ $ " 2""%"% ! " +"&"&"+ * @ $ ! $ .$ ! $ !$ @$ ! ) /) !0 %& " ! ! " ! @ ! $ ) $ ! $ ) $%1 + ) ! @ !! ! ! !! " ! ! " - 5 3, ) ) ' # ' ") = 2"""% A !$ $! @ ! ! +"&"+"% !! $ @ @< 3%"* "# ! $ @ ) $ $$ ! ! $E @)$ $ ) ) $ $ "' ) $ ! ! 5%)%E )&E2 )2E% )% E%2 )%2E " ! @ $ . @ = / $ $ !! $ ! +"&"+" # $ %K! $E@@ ! ) @@ @$ ! ! " $@ G )%K! $ .' )% C /" ! $ @$ - # / ( A ! @!" 2""&"% @ @@ = ) @ ) !! ! $ @$ "< ) $ +"&"+"& 7$! !$ @$ $! )$ ! $ ! @! ! .!3 ) / @ $ " @ @ !@@ " * ) = A ! @I $ ' # - 2""&" $ " ! $ +"&"2"% 9) @ $ $ @ ) $ $! !@ ! "< @!@ $ @$ " $$ $ $ ) $) ' # . , 3 ) ) ! $ !$ " +"&"1"% A !$ ! ! ) $ - ' / " '@ % )! ) = ) <$ !!(! $ @ ! ! !$ @$ )! $ ) @ $ ! 2""+"% ) @ ! E ! = "* ) ! " @ @ $$ ) $ @$ @ ! R 3 ! % ! $ @ ! ! R ' )$ @ "*3 @ @ $ $ ) ! !@@ ! $ $ @ . @) $$ @) $ " )!3 /" $ ! $ @ ! ! " 2""+" # = ) @$ $ @@! @$3 $ " - ( $3 ! R ' ! $! @Q$ R = $ $$$) @! E! @ - 3 $3 ! $ " < !$ @$ A 2"%"%"% - - / ( + )$< ) ! 4 C" 2""2"% # @ $@ $ !!! 2"%"%" !2& !$ )+ ! @ $$ @ $ $ $A $! " " $@!$ ! 3! @ ) $ 2""2" ' ) $! ! $ !! $ " ! ! ! @ " 2"%"%"& 9! ) $$ . $ /) $! < @ E!@! 3 @@ ) ! $ .@/ $. / ! ) ! @ ! . 3 ! ;H < "9) $/ ! ! @ $@! $ @$ " . @ @/" 2"%"%"+ < $!$ ! $! A !$ @ 2""2"& ) $@ @@ @ @ ! $ ) !$ " = @ ) " ) @ ! ! $ "# 2""2"+ @ ! @@ $ @$ ) ! $ ! ! @E $!$! @! !) @$ @$ " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @+ 9< ? # %< @ - . "+ 30 2""1"% # ) !@ ! $ ! $ @$ ) ! @ @$ " @ ! 4 )$ $ ! " 2""1" #! @ $ ) 3 @ $ E $ ) ) "#! $ ) $! @ @! @ ! " 2""1"& # $!$! ! @$ $ ! $ @$ $A " @ ! ! $ @$ " - > ") * 2""0"% < ! $) $ !@ $ @ $ !@ ) @ ! " 2""0" # @E @! E $3 $ ) ! ! ! $! " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @2 9< ? # %< %627*1 @ %! D %! D -:D 8 , ; %!(D -:' ) ; %!-D (-:2 ' 2 ; %!3D --: ! )&; 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= 9< ? # %< ! !! ! !! ! !! ! !! ! !! ! !! !!!! ! !! !!! ! !! ! !! !!! ! !! +* !! 0.- 4 !!! " !! !! !! &2&>2&3 45 4 " !! " 01 -- / &*+ & (*& !! !"# ?$!!%&'(&)**+ !! , -,. 0 +0 !! Pinewood 7%00 & '- 00 !! ! ./ * !! !! ( ! ) '- " 8 <<&( 5;5 &( 9592 &)( 8 8 &( :: .3&( :: . .3&)( 3 3&)( &)( 191 9 . &( 95 19 95 : 07'07'0 56 5 " " 23 .. : 1 '!')0'*' : < 5; !"# $%!!&'()'*++, - .-/ Pinewood !" #$ % '. " 6 6 6 &+( " 3&)( 66 &))( 22&0( 6 6 "" 3 &)'( " 6 " 6 6 " 6 " 6 6 6 " 6 6 6 6 6 " 07'07'0 56 5 " 6 6 6 " 23 .. " 6 1 6 6 '!')0'*' 6 6 " " 6 " " 6 6 " 6 6 6 !"# $%!!&'()'*++, " 6 - .-/ " 6 6 6 " 6 " 6 " Pinewood " " !" #$ % 6 '. " : : &)( "" 3 .&,( 2 2 &!( 5 2 2 &,( " &+( " 2 ==2 ==&'( :: &( 5 " 5 : 07'07'0 56 5 " 5 " " 23 .. " 1 '!')0'*' " " " " " " " : !"# $%!!&'()'*++, - .-/ " 5 " Pinewood : !" #$ % " 5 '. " 5 :8 : &,( :6 55. &,( 52 == 2&)'( &,( :8: = 2&*( 5 :6: = 2&0( 5 ""= 2&)( 5 :8 " :6 5 5 5 :8 :8 5 07'07'0 56 5 " :6 " 23 .. 5 " 5 1 '!')0'*' :>, 5 5 :8 5 :6 5 5 :6 !"# $%!!&'()'*++, :6 - .-/ 5 5 :8 :6 5 :8 :65 Pinewood 5>, :>' 5 !" #$ % '. < 3< ) 9 ""# @ ""3 4"3 #"3 ""4 3"4 $ ""3 4"3 #"3 ""4 3"4 $ = U E E E .; )+ / * *$ 2 & 4 & % 8 2E% = 8@ U @ E E E E .4 4 )+ / =!!!! 0 1 1 8 % = $ = F U @ E E E E . 4 )+ / F E E E % % = U E E E E .9 @ / F 3 %& %% C + 8 %2 (( U EEEEE. = )/ 3 C %& % 2 8 %2 H % % E ( %= @E + & - % % &E2 B$$ % % E % % @ = 7 E % E % % = E % E E < R ' ! @ 2 1 0 8 % @ = @U E E E E 3 .9 )+ / 4 E % % % % = U EEEEE.; ! ! ! )</ 4 E E ( % E %E B@F U - E E E .9 $ + = / == 2 + & 4 & 8 2 = E$ F U E E E E .9 $ + = / @ 3- +C %0 %2 @ = '@ E ( % E E %E $ @ B 4 % 2 E + 2 @ * @ C 0 C %2 % 8 % E%2 = $ =!! %+ C %+ C & 8 = : % E E E %#B @ + + 3 & 8 2 $I @ = U E E E E E . @8!= )/ F ! + 1 + 2 8 2E% $I @ 9 E E E E % R ' G 4 F! + % & 3 + 8 2E% $I @ ! U E & %& (3 & .<$ ! @! / ! E E E % %E @E U @ E E E E . ( ) 4 / U]7E$ @G)E > F* % % % E % = F * % ( % % %E = 0 1 %% - %% 8 % @ R ' ! % E 4 %E R ' )$ ! B U E E .9 R ' / E E % % % R ' ! *@ E E E % % * %% C 8 %1 = @ : C 0 1 2 8 % $ %2 %C 1 + 8 @ 1 1 5 + + 8 C $ % %& %% 0 8 F *$ % % E E E 8 %E %% %& - 0 1 8 %2 * ( & % 8 &E2 * 1 5 % + 8 2 $I @ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @<% 9< ? # %< < 3 0 @ ;H ! % ) $ !@ ! $ 5 %E% M<M2 %%E% MM+ % %M% M=M& % %E% ) M:M % ) %M% ) M8E% ! $ @ 3! ! " )! 7D)! 0 H &2)+ 8 % B$$ ) : 9 2)C : F* +) 8 % F * &0) 8 % * 1+) 8 % ! . 1/"*$ @) !@ " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "188:#7F#: ":9= @% 9< ? :! %% * + & * @ * @ < ! " # ! $ $ $ %&' ( ) *% +, -++. / 01&1%2&%'3-++. / 002 22&% " " 4$ $ 0 + * @ @ % 83 % # % "% @ % " * @ 8@ @ % "& < 9$A % "+ % & @ % &"% = % &" ' % &"& + < +"% = +" ' +"& < !* @ & 2 = + 2"% !' @ + 2" @ = + $%7 $ ! = $* @ . C/ $&* @ .7 C '$ / $+H* @ $2 = !* '@ % H< !< '@ H $)) < 3< ! 7 C '$ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= 9< ? # %< * @ $ !! @ $ @ !! ! ! @ " %"%"%"% < @$ ! A ) A ) $< ! 7 $ C" ! %B$ C $ ""%"+ < $ ;H $ * ! = < % C% ! ! @@ ! " . /" !! ) $ )A $ G ! @ ! @$ ) @@ @" %"%"%" < !! $3 @ $ 7 $ '$ $ ) @ @ ""%"2 : $@ !! @ !! ! !! " ! ! @$ @! . +/" R @$ " # $ % & %"%"%"& < !2 $ @ G+0! @ "&"%"% ! 5 $ @ ) & !E "7 ! $ $ $ ! @$ G ) @ $! $ " $ $ ! ! @$ !$ ! @ ) ! ! G $ @ "H @) ) @ ) @) ) ) $ !" ! @ ! @! ! @ $ $ ) $ ) (" $ ! @$ " %"%"%"+ H ! ! @$ = ) @ ' () ! = ) ! ! $ @! " ! ! = @ .3 "+"%"% '@ ) @! @ $A !! @ /)$ ! ! " & $ ! ! A ! $ @ " @ ) @$ ! " + @) )! !) $ !@ ) $@ !! $ ! "') 2 ! @ " " "+"%" < 3< ! ! $ @ " %"%"%"2 # @ ! @$ ) $! "+"%"& '@ % ! @$ @ @ $ " ! "'@ ! @$ " $ @. @ $ @! @ / $ !! ) @ " # *+ # &"%"%"% < !3 @ ! @$ $ ! @ @ H 8 "%"%"% < $ )< C) ! = .;=H H8=/) ! %B$ .8 ) 0/"< @ !+ A .3 @ ! , ! " %C++/"9! ! @$ ! " ! &"%"%" ' $E$ ! ! $ ! %B$ ! C.8 /" %) @ 7 7 .77/" "%"%" !@E! @ ) $ @ $ ) # $ #B "# !@! ) &""%"% < !! ! $3 @ @ ! @3 !! @) ) ) @ E 7 $ C"M $ !: $) !@!! !)! ! ) ! ) 4 '$ $ !$ $ @ " ) ! )$ " !$ ! $ @ " &""%" @ $ ! $ ! %B$ .8 ) C/ @! @$ " 0 $ $ $ "B$ $ $ " ""%"% * @$ ! $ $@ !! @ I @ % " &""%"& @ ."@"$$ ") F$ ")% C / ! ! $ " @ ""%" H ! $@ ! @$ $ ) $ )$ 3 !$ @ ! .@) ! ! " @ / @ " ""%"& < $ @$ ) ! @$ !! $ ) $) )@ ! @" %$$)="4") . / = ) 8 E< F$ )F")F$$ ):)*" 8 )4".% C/ @ 5< ! !H;H M 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @% 9< ? # %< * @ &""%"+ < ! )$@ ! ' !) :8 &"#; E ) @ F* @ @ !! " )$ H F B $E " $ !! ! !! $@ " =!! * = F ! &""%"2 8 3 ! @ @ ! " ! ! @) ! ) E F : 7 ! )@ " ! ! $@ !$ = F $ @ F! ! @ ) * @ $ 4 E !@ ! $ "<! !$ ) ) ! $" = : @ == E &""%"1 9 )$ A $ ! ) @ !9 @. 9/ +"""% : @ $ 7 $ C '$ .< /) !+ !$ "' @ @ 3!$ $ ) A " $" (' !) :+"# %"C; &""%"0 ; ! 3 ) ! $@ ! @ ! = @E @ == ) $ ! ! ! " F* @ # # H F * F B &"&"%"% 7 $ ! $ ! F =!! ) I@ @ " @ ! " F F*@ = F ! ' ( $)) E F *@ ' = F * @E F! B@F : 7 = $ +"%"%"% !@ !$ $;=H H8=. I 77$ /! ! ! " E$ F $ ! '@ $ @ E + )*0 * @ ' ! 4 E + 0 * = : @ 4 E @ % "& 8! ' ! % *! +""" @ @ ! @ ! ! = $ % % *! ) @ $! 3"" H@! & %"2 *! $ $! &5! !. %/) @.01/)@ +"""& .2 /) @.&+/)$ .&%/) .& /)@ !.C/)$.2/ $E @ +"%"%" $ @ ) .2/" !"* ! ! ! # ' ! $ ! ! !)! ! A ) ! +"""+ < 3<" $ !$ $ @ ) )@ )! " '@ % " ' +"""2 !@ ! ! @ ! " ' ,) $)) 9?5 77; +""%"% !! @ !$ ) @ !@@ ! +"""1 = ) ) @! 0:= % :=$ ! @! @$ " !@ ) $) @ " ! 0"+2 . 0"& / %% " !@ !!@@ ) @ ) @ ) ! ": @ ! $ $!@! +"""0 F $ ! $ ! ) @ $ ! " @. R R' ! /))@ !!. = /"7 $ ! @ !@ ) G@@ R ' G ' ( : @ @ .8 ) C/) !& $ " &3 ! )$2 )@$ 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @ 9< ? # %< * @ = G @ $ "< +@E ) @ ) @) ! @ ! F" ! $ .47== $ 2/" 9., 77; +"&"" @ ! @ H < .</1) I @ ;H<) ) +"""C $ % + ) !@ &"2 G ) ) )!@) +:=" ! ! ! ! . H 8 = M8 = )4 +""" ) !$ ! @$ C0/" = $ @ @ -D ' !) F @ " @ @ ! )$ $ ! @ F@ @ ' 0 +1*0 7D) & &% !! 2@ ! @ $ ! H .%/ < $ R ' ! " @. / < $ #9>< 77? F* .&/ < $ +"""% = ) @ ) &:=" $ %"%2 +"%2 ) !@ +" 2 " . / # +"""%% 7 $ !$ @@ : $) 3 ! ! $ ) .C/ < $ @ )! @ @ ) ! @ $ = F @"<!! @ F*@ .%/ < $ $"' ! @ ) $!@ @ ) : .%1/ # < $ 2! @ ! R ' " ' !. %/ < $ '9 77? @.%1/ % < $ +"""% = 3 ! )$ $@ ) := @ +:=$ ! " ! 0"2 . / % "& " @ .1/ # +"""%& 7 $ ! ! ) @ )$ )@ .%/ < $ $@ @ ! " $ $ ) F .1/ < $ ! ! ! R ' " ! ) % @@! = A F .%/ @"9! @ $ !! !. %/ $ @.&%/ # ! @ ! R ' @ !@$ = @ " B .& / # $ % .%/ # +"""%+ : @ ): $ 4 ) $! @ !@ !.%/ # !@@ ! $ .3 $! / " $ @ '$ "7 $ %2 $ @ 2 @ 4 $ ! +"&""& 7! $ E ! ! !" $ 3 E "7 @ ! < ! @ " ' # $)) 30 +"&""+ 7 ) !! @E ) +"&"%"% # )2 !$ ! $ @ )! $ !!@ ) $ $! ! C $ 7 $ C '$ " "# ! H@! .! / ! ) $ !$ " " ' # # , +"&"%" @! @ $ ! "F) +"&"&"% ; @ ' @) !2 ! @$ $ ! $ ! ) ( ! $@ $ @QR! .2E2+ /) $ + ) ! $' .% C / " " $! ! .22 ' # ( / $ $!@ " +"&""% 9! $ $! @ ) $ $ $ !! .!3 ) %! @ ) 247==. / ! ;H5 != = E 0 ( !# > ( / ! 1 @ H . 0/ @ H < E % 0 @ H 8 = M8 = .4 C/ +' )4.% C /< !< @ 9 @# ! != E !9 @ = ! !* ! ) @ 93! .M ):! / 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @& 9< ? # %< * @ ' # ' ") = 2"%"%"& 9! ) ! @) ) @ ) @) ) ) +"&"+"% < ! @! $ !! $ $ !"9) $@! @$ " Q= ! !* ! ) @ 2"%"%"+ < $!$ ! $! A ! @ 93! R.8=I M8=):! M ) C/ $ !* ! " $ ) !$ " = # ! @ ) $) @ ) @ ! ! $ "# ! $ " @$ ) ! $ ! ! 3)* 0 *F' ! "' $" 8 > 8: : ; ' ; - * ) * @ & 2""%"% ! @ $ @ 2 ! " ! $ ! @$ ! @ 1 % " ! @ ! $ ) % C ! @ !! ! ! !! " @ &% + - 5 3, ) ) 2"""% A !$ $! @ ! ! B & % "# ! $ @ $ % 2 $ "' ) $ ! ! @ $ . @ = / $ = $ % % $ !! $ ! ) ! % @@ @$ ! ! " - # / ( +"&"+" # ! ) () ! @ 2""&"% @ @@ = ) @ $ " ) !! ! @$ "7 $) @ ! @ $ ! ' # - $ !@ @ ! 3 ! "< ) $! +"&"2"% 9) @ $ $ @ ) $ $!.@/ .!3 )@ $ !@ / @ @$ " !@@ I!@ " ' # . , 3 ) 2""&" * ) = A ! @I $ $ +"&"1"% A !$ ! ! ) $ " ! $ " '@ % ) = ) !@ ! ) @ $!! ! ) @ $ ! . ! "< @!@ $$ $ / " @ @ $$ ) 3 ! $ ) $) ) ! $ @ !@ @ . ! !/ $ !@" !$ " $ ! $ @ ! - ' ! " / 2""+"% <$ !!(! $ @ ! +"&"1" @ !@@ . &"""2/ $ !! $ ! ) @ ! E ! = "* ) ! ) ! ) $ ) $ @$ @ ! R $! " @ "*3 @ @ $ $ ) - ( $$ @) $ " - - / ( + - 3 2""2"% # @ $@ $ !!! $$ $A $! " 2"%"%"% < ! @$ A )$< ) ! $ 7 $ C '$ 2""2" ' ) $! ! $ !! " ! @ ! ! ! ! ! @ "< @ C) ! %B$ .8 /" E!@! 3 @@ ) ! ! @ ! . 3 $/ 2"%"%" !2 !$ ) ! .@! / ! ! @ . @ ! . ! A /" $@!$ @/" $! @ @) ! 3! @ ) $ $ @ " !! $ ) $ ! ) @ " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @+ 9< ? # %< * @ 2""2"& ) $@ @@ @ @ ! @ ) @ ! @@ " - . "+ 30 2""1"% @! @ @ @ )@ 3 )@@ @"B) @ $ $ $! @$ ) )$ )! "# ) ! ! @$ $ ! " 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @2 9< ? # %< %627*1 * @ %! D %! D 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= 9< ? # %< ! !! ! !! ! !! ! !! ! !! ! !! !!!! ! !! !!! ! !! ! !! !!! ! !! +* !! 0.- 4 !!! " !! !! !! &2&>2&3 45 4 " !! " 01 -- / &*+ & (*& !! !"# ?$!!%&'(&)**+ !! , -,. 0 +0 !! Pinewood 7%00 & '- 00 !! ! ./ * !! !! ( ! ) '- " 8 2 2 9-9 - - . 8-8 .2 8 -2 2 - 0:0 : . 8- 8 8 11 00 1 8 8 9- 44. " ""; 1 <=1 8:8 := ' 5 0: 8 +6')6'7 45 4 " " 12 .. 0 '*,,'*-, 8- 8: 5 " 0: !"# $%!!&'()'*++, - .-/ 8- 0 8 4 ! "#$# %& '. < 3< ) +"# %"C * @ "# "# ""C " "C $ "# "# ""C " "C $ .= / @ % E 9 @ %C %2 0 E E % '@ = 4 % E % H @ % E B @ R ' ! 4 % E E - ( E E E ' @ = == ( 0 1 + @ E E CG E 2 ! R ' )+ U @ % &% 1 (- F @ R ' .F / " E E E '! B E (" %2 F @ E F @ % 3 R ' ! =!! 0 % % = F @ + 3 % E E E $ ! = B@F 5 % E 2 F ! & # %+ E$ F % E - % E E + E B @ ! ! = '@ E % E F! % # C * @ 54 +2 +1 + .= $/ E E E 9 = : E E ! % E % @E - % E E F @ &C &+ & && F* % ( % -C .2 @ ! @ / F * & 3 2 & ./] !@ 2 E E C R ' ! G @@! '$ )] 3 % # C @ $ ! = F*@ E @ E = R ' *@ E @ % * " + : % 1 + 4 $ % C %0 3 $ % % # %& ' ! % % C R ' ! = @ & 4 @ E 2 4 % % E R ' ! F 4 + + E = F %1 0 3" &% = @ % 0 C ( = @ = @ E E ( B @ ! = E E E %@B @ ! = @E %% %% 0 = @ 7 E % E = % E E = 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "0*#7 8#7F#: ":9= @<% 9< ? :! %% , - " #$ #$ % &#$ 2 0& . .& & <&& ( : & . & '& & /& & =&. %0 .4$'&'2 ' : 0 . 3 $&// ( $ &/ 2 2 ' : 0 & M ? !!" 5 & / 83 ? / !!" 5 & & :$' -8 & - # $ !!" 5 & & :$' 82 ' .'@ &/ : & & (/ . A 2 '()!*# '& ,'/ : :$ / ' $' :$& / $ $ .2 ' .'@ & ,@ &&:/ $ ' ( 0 ' $' :$& ( & /& & . $ /. $ ( .2 ' .'@ ((.: ( & : &3 ./ $ :&/ / (&/3 /& $ $ & /&$ ( ' . '& /: :$& ( ' 2 )0:3 &/ : & '& & .( /0 /:/ .' & ' / /& 3 0'.' 0 /4 ( '& ,&.'$ & :$ / : & 0' '2 2 !+,- .*# ./' & 3 '/ & (/ $ (&3 /0 &.' ( ' & ' & '&/ & 0' & .4 / $ .2 /&.4 0' & & $ 0'.' $ ( : & '& &$ ( &.'2 9. & .//. ( ' & $ & 2 ' .'@ ((.: &$ . ( & &/ .3 ./ $ & / $ 3 $3 .&//& ( &3 & '2 9 .& &4 & & 0' ' & ' &/' $' ((.: ( ' :$& 0 ( ' 0&' 0 2 2 )+((!*%& & & ( &/ ( & 0& &2 ' . ( '&//0 5/&.8 & ( /@ 3 0'.' & /&. ' ' $ & /:& 2 9. & &&. ' & & (&// ' (/ 2 * ((.: & //0 & 0' 0' & ./ . 2 * ' ./ 04 0//2 ' (/ & 0&3 0' & ( $ . (&. 3 ( ' & & . 0' & . / ( & 2 #/&:/ (&/ ' / 3 / &/.'/ ' (/ & ( ( ' & & : / (@ / 2 ' & & </ ((.: .//.$ &/ ( /& 3 /& 0&3 ,' $ 0&3 / 5.&// ' / & & & . &83 3 ':(/ & ' $ 04 0' ' '$2 !" 2- % !.)+((!2 *. ,:& 5:8 /$' / & &&. . &/ . , # $ !!" .&// '2 ' / /&,:/ /$' & & 0&:/$' 0'.' .& ' &&. ' 0&:/$' '&/ ' &2 ' / & : .&.'$ .'& (// 0' .& & $$,& & ' $ ' .'& / ' & & & <& 2 / & 0 ( & /.. & / $&2 $' &$ ' $/ ((.: ' ( . $ '2 %& ! & ' ( )( ' * % ! +, ! -+ 3 .4$'&' / %/& #.& 5678 ./0/&1/0/ 2. 9: & : /& ;/$ # $ !!" !" & 2" .' $ '& & : ' .&/ ( $& ( : & & ' /& .&D 0' ' (/&/ . . ( &: &' '& ,&: . ' $ '& & 0// &/ & & . : & 2 2 B:&//3 ' : && & &. ( (/ 3 0 /& & ' $ & &/ $ ' 0 ( ' C& &&3 ',& ' * 0& 2 9 ( 2+ # %0 3 $ '& & & & & (& & & ( & ' 0 /& $3 ' $ : &/ &.,'& & ' &3 &// 3 ' . ' &. M ' ( ( ' $' ' : && & ' /. $ /&2 .& ( ' . ' ( $&/& 3 0 /& & $ '& &2 &&$ $/. ( (/ :/$ & & $ '& &2 2 ' $&/& ( :& $ @ &/ 2 ' ( (/ ' ' ( ' 5(/ 3 3 & 2 ! ' $ '& & & %0 & /4/ 3 ' & ( && (& & 3 ( '$' :&/ 83 . &' // .(. &. ( : & ./$ D /& . &/ &/ : & ./$ ' /.&/ &&2 ' (/ / $ ' ',& & ( ' 0 /& 5(/ -8 ( ' '2 ' &3 '&: 3 && / . /:& & ' : & '& 2 9 ' 0 &$ (/ 5(/ & 8 ' : & $(.&/ '$'3 '0:2 2 / & &// &/$ & /. $ /& '& &&/// 0' ' * 0& 2 )3 . :& $ ( ' 0 /& $ & ( ' ' $0 & ' ' &. :$& &// & &43 & < 0' &/ & ' ' & &// &/ /&2 ' (/ : & &. ( 0 /& $&/& (&. '& & '& & ( : '$' : & $(.&.2 2 / ' /&$ (/ ' ',0 ( ' 0 /& 2 #/' $' '&:$ & && / ' 3 ' (/ & & ' $& $0 .' ' '2 ' & && ( @ 0 $ & =&. ' 0 /& $ & ' && & .&/ & /&$ ( : &2 ' (/ .,. (&' & : / ( ' /. ( ' /.&/ &/ &&2 2 ' 0 /& 0//, ( & ./&/ ( . & $3 :'/ & ( &$2 ' & ./&$ 0' ' 0 /& & ' & ' ' .&/ :& ( : & '& & & 0// & .&$ &// && ( /&:/ .&/3 0& & ' ../&2 &/$ ( : & ' 0 /& $$ & .' (& & '& $' & &/$ $& &/2 2- ; $ '& & & ( ' . ( 0 (& M '& /0 & /:/ & & . '& &//2 # ./&. <&/ & ' $0 . 0' & (/ 3 ' <&/ ./ ' 0 /& $&/& (&.3 & :$3 : &4 & '2 ; $ '& & /& & &/ / : & ./$ M && ( & . 0'.' ' & ' &/ &. & . ( ' .&/ : 0 (( &&2 2 ' $ '& & & ' '& & $& &/3 0' ' :.&/ . $ $& &// ' $' /$ $&3 &// ' & /&$ ' & 2 ' // & ' (//0$ &$&A 3 .4$'&' / %/& #.& 5678 3 .4$'&' / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" / #$ $ 5 .)+1 '&3 . &3 $ & : /&$ <& ( &$ '& &/ .&/ ./&, :2 9 & ' . :/ 0' ' & / (/ 3 (&: & / 5'8 ' (&/ :/ 0$ ( '& & & / &( /*" 0++ +1 &$ & & /' /& 0 &&2 9 ' ',& ( ;$/& 3 ' ..4 . & / & &. $&/& '& &3 ./ $ ,& 3 (/ &$3 & :$ & /$'/ $& & 0' ' / ( :$& .:2 ' G&&// G& / & 2 2 # < ' . &<& . $ ' : 2 ' / && 0' & / /$ 0&& 2 (&/ &&/ & . 0' ' & '& O&&// .P & ' & . & </& # < 2 2 2 < . & / (&// & G&&// .&/ 5 # < 82 ' &A 2 2 # &/ ( -" : & . 0& . 2 B( '3 + & ' M / .& $' ' /$' &2 & / &.& 0' & / /* (2+3+ & /$' / /&:& ( &// /& 3 .&// '/ & /&( / 0 / / '&$ 2 2 :&/ .&$ ( : & & ( & $(.&. & ./$.&/ &2 ' .&$ & </& # < & ' . $ . & 0 <& 2 & /&( / :& .(& & 0:/ ( &4 , .& $ /&( $&// 2 2 G : & . '& & &(( . & 67 ; & /$/& 0 . $ ' : 2 C/0 & &/ &$ /$ $& 2 2 G . / ' ' H&& 4 5'3 +" D &3 ++ 8 0'.' '& &$ / /&:& ( (3 ( /:& ' & ( G&&// ; &$ 3 G&&// I /& / G&&// & & ,/&: @ (&/ :0 & . ' : 2 & / & . $&/& . 2 2 G ( ' . . $ ' : & 67 : #. %/& . & / (/ /&:& ' $ ( 0& 567 : C 3 +++82 & ':(/ H& $&/& 2 2 B . '& (&// /&. G&&// G& / .&$ G& 5 # < 8 . 2 )& ($' B&4 .4' ( 3 & & /&:&3 ' ( & .4/ &4 3 & ($' &43 & & ' &/$ //$ ' 42 ' ' & / $3 ' :& .'&&.. H,'& $. '/ ' &4 & ' . ( ' . $ ( ' / 0' &. &// $ 2 & //0,(&. '//0 /& 3 .' & .43 . 9 . .& /$,& /' '& & 0' & &4 & & & .& ( '& & '& & ( & ./$.&/ $(.&.2 ! ! " /.' ;&/ &4 2 2- ' . '& & (&// /&. G&&// G& / .&$ G 5 # < 8 & # $ %,&4 & 0 & ( . 2 ',0$ ,'& (/ & & .&&/ 3 0 ( & :& ( /& '& & .2- 0 & 3 /.&/3 ' ;$/& & &.' ' ' / ( .&/ &$ ' * /& 2 9 '& &/ ( .&/.& & / $&/& 3 & ./((3 / @ &3 & 0 /& & ./&$ & . ' '& & .&/2 ' & ' (.& '& :( & <2 9 & ' '&$ . & ./ &.& 0' &$02 . & /& '& .. ' ;$/& 3 &/ & ' .&3 &/ ( /& 2 9 . . .'& ' $ 3 &&/ ($ & 0' & ./& .2 # / // @ & ,. &3 (/0 : & ( & :& ( .3 ./ $ :& //0 . 5#&.&82 9 . &3 '& . & 0 & & . . ' ',& ( & & & & /' :0 ( & : ( ' / ( G&&// .&. .2 3 .4$'&' / %/& #.& 5678 3 .4$'&' - / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" 6 $ # 2 *& : & '&: &/ : // .,'& & @ 2 <&/3 /& @ ' & . ( .& & & $ && & 0// @ ' (/0,.' $&/& & & && ( &3 (& / /2 /&/ 3 &< /. / 0// ( & & /&:& & & / 0//3 /4 ' 3 &.. & $ . & ' &. $ & / $&/& 2 2 @ / 3 & '$' : & '& & &. '& && ( & $/ '& & 2 2 ' .&/ ' .& & %0 3 &/' $' ' :&// &. ( $&/& 3 0 /& & $ ' ' '& ' '2 # <&& ( ' ./$.&/ &.& ( ' 0' . '& ' (&.2 2 9 ( & '& ' 0&' . '& :&/ $ !!" 0 / '& (&: & / ( : & &.: M & : / ( : & : 2 # $& & . 0 /0 3 / ( 3 & & $& & &2 '3 . 0' ' /0 ( : !!"3 & '& ' / // '& : & ::0 ( ' & ( ' : & (& & & %0 2 9 3 ( <&/3 0'' & ( ' 0' . 40 ( ' & /&.4 %&4 9 & 3 & $& &/ .&/ : 0 / 2 $ 2 '' ' &. &// .& 0// ' :/ /& ( ' : &&2 ' '&: :0 & & ( ' 2 )0:3 ' & ( ' /3 ./& '&A ' :/ ( ' 0 /& && & & =&. (/ 0 / .& $(.& / : & ./$ D ' / ( ' $ /& 0 / @ &// &&$$D ( ' ' '/ (/ /4/ . : & : '& / ( ' ' $ &&/ $& 2 3 .4$'&' / %/& #.& 5678 3 .4$'&' " / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" $7"8 #$ $ 0+ (9( !. 2 !, 3- 0+ (9( !. 2 !, & & ( & (/0 3- ) ( & 0 :& ( . .+; , &$ .&/ 0 / / '&$ .!, ! :& '/3 .4 & ' #&.& & ' =. *'& , .&// *'& &@ &.&2 H& & '&:& ' =. '& & % 0//0 , &/ /& #: # * & /&( / %/ $ . -, & (/& / G &$0 5. .8 , & ' . ! & & (/& / 0 / / '&$ ! 0 0 / /&:& ( & & (/& / ( & /& . /&:& ( & &.' & ' & & /&( / ( $& , : . & /&( / :& &.&.& (, & /&( / :& &.&.& & 0:/ & ,/&: .4 .&/ :& .(& & 0:/ '/3 .43 4&0 & ' $''& 5/& /.&&&8 & , &' &3 & &/ I..& :.' +,- !, /& & ' . *// .3 .&// *2 ((.&/ , ' .- , /& & ' . +/- +, /& 0/& '& & & *&/:&.& , .&// *&/:& /: +0- &, & & ' . :.' , ' I..& & &' 1- , /& & ' . ( & 0 :& ( /0 /& & ' 0- % /& &' & ' & & ,/&: & 0:/ :& ./:D 0 & & . -, 2 +3- B&$ /& & ' . % ' &. ' , ' /&:& ( $ ' ( )&/@ /& & . ./ & + ., +0- , /& & ' . &:& ( 3 &' J I.&D & / #! .0 - , /& & ' . & :& (/0 (+, ) ..- , /& ( / 0 G& &.& 0' / &4 + , ; +, ! (/0 ( & / & & .&/ & / & 0:/ .&/ &4 , .& $ /&( $&// .+, & & / / &// :$&3 .&// & ' < . 5 .48 , ' (/&$ 0 /& $&/& (&. ! & 0:/ &:& :/ ' $ & & / ( & & / / /0/& &'3 ' & 3 & '& :& ( ' &$ & /&: & 0 . ! .&// ' $ & ' $ '& & & / / .4 $&/& 3 .&// ( & / '&$ & ,/&: 3 .&// &4 % & / / &//3 &4 :$& /0/& && & '&/ % & & &/ . % ' /&:& ' /&: ( &4 % ! & / / $&/& 5(/ .&// '&$ .'& # & 0:/ :& /$ (&/8 +, % .&// 0 0 /& & . ,:& /&:& ( $& 0/& 4 5 $&/& 3 0 /& 3 .2 ' /&:& ( +-, .& $ 0 & / .4 $&/& & .&&/ ' /&:& ( ' ( $& ' & &/ . ( . & H& '& & ..&&// .( /&:& ( .& $ 0 @ 6! 45 & . ( $&/& (! ! @ /& & & . + -;, +, .&/ /&:& ( &// /& 3 ./ $ ! G/ '/ G/ & /$' / & 0 , &// .' 0//0 : (;+, )&/@ / /&:& ( .& $ D & / 0& C/0 .&/ & &/ &$ /$ $& 3 .4$'&' + / %/& #.& 5678 3 .4$'&' ! / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" 0+ (9( !. 2 !, 0+ (9( !. 2 !, 3- 3- :+,, &:& @ & '& & & / & ! /3 .3 .4 . , / / @ @ &:& @ & '& & & / & /3 .3 .4 . , / / @ @ C&/& : , .&/ H& $&/& &$ / .&/ /&:& ( (3 ( & ,/&: &:& @ & '& & & / & / @ # & C&/& , , & C&/& & & // / :& (/0 & /&:& & ,&@ &. #, +, ( $,'& & . & / .&/ & . $&/& . ! @ , /&:& &' ! & . $&/& . & '& & ;+.+, 8 H& '& & & &/ / &:& & / &4 8 0/& #, &' & &$ :$& & 0 / &3 03 '& & : 0' 8 8 &' & ., % 0 $ & 0 / . # C&/& +, # /&:& .& $ :$&D & / & (/0 ! & 0 / . # ! /&:& & &' & & ' $ % # /&:& & &' & & ' <+2 , 9 !! @ / ( / 7 . &0$ $&/ . 9 @ / ( .&/ 0& ' $ : H&3 & 0 , : && & 3 . 0 3 .&// ! & (/ & ,&/ $ '& & & (/ $&/& & -, + ;, & '& & , & / (&/ & / .4$ ! &.& 0' ' . $&/& (&. '(/ /&:& @ .$ $&. & & # @ .+, .&/ /&:& ' $ ( 0& , & ' ($ :$ 0& /0 :$& &.& 0' ' . $&/& (&. :;!, &.& 0' ' . $&/& (&. G/ # /&:& ( $ :$& & /& 6 & ' $&// &&/ %+, ;+(., / '&$ '& 0 /& C&/& ! 8 8 /&:& ( ' ( & . / &.& 0' &4 /&:& & ' $' ( ' ( & &$ & ' #'. /: ! /3 & / & /& $' :$& /&:& ( ' ( . ( ! ;/ ' '/3 .&// &/ -0- &.& 0' &4 &.& 0' (/0 0 & 0 & :&// $ B&4 ,/& & 0 ! $&/& . ,&.& 0' &K ! ( & 0 &$ ( $&/& '& & ! &' & & 0 /& $ '& & $$ / &' & & 0 /& $ '& & & &.& 0' &4 &/ & $ '& & & 4 & &.' ( . ! @ .3 &/ $&3 & & & ( &' 3 $&/& & ( 2 %&/ ! &:& @ & '& & & / & :$&& & &/ & & / @ ! * $0 , & / 0': ' $0 3 .4$'&' / %/& #.& 5678 3 .4$'&' / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" 0+ (9( !. 2 !, 0+ (9( !. 2 !, 3- 3- ! / '&$ 3 &// &.& 0' $$ <: / &(+, # $&/& &$ 4 $&/& # $&/& ) &// 4 $&/& # ! $&/& ; (., , ; %&..4 / ! & / / '&$ & " *& 0 0 $&/& . & ' +, &#%# ! &$ 0' :& .(& +(, : $# 8 & ($' /&:& ( (' & 0 &$ ( %# & & ' +, /, $ .4, /&:& ( (' & 0 &$ ( .&. & /.' , .&// 43 (. . $ ' &. /& (( & /.' & &/$& $(., H$ & /.' # $& & &$ ( '& & & /.' , .&// 43 (. . , # ! ' ; ' &. /& ; :& . # (( ; ' &. /& & &/ & ' :,+, ) ,0$ /.' & )& .&/ B&4 * / ($' ) " ! & & &$0 % -+, $+(, & ($' .&/ &43 & & ' &/$ ' '&&. /&.4'3 '&0' & ' &. ' &% # 8 0 +, : ! % *' . & ' &. /& (, ! &: &/< . & & ' (/0 $&/ ! ' . ! ,&/ / @ &: $' ;&/ . ! 0',&/ / @ ! L//0 '// ' &. /& *& / . & ' &. /& ! . .& @ & & //0,(&. .&/ '//0 /& 3 .' & .43 . - I,% $ ' &. /& & $ G $ $ . , ( / 0' & ./& & L//0 H$ . C & &0 <.&:& 0 /:/ $ ! ! " /.' ;&/ .&/ &4 ( && ( # & ..& .&// B&4 . <+ , & &0 . /&.4 &2 $&/ . & &0 &0 & ! & & @ ,.4 % $ :& (/0 & .&// (&// & 0 2 #/ / % $ &//0 .&4 $&/& &/ '& & % $ ' &. /& (., ;&/ . ) 2 G /& 3 / ; & 0&: ' &. /& , .&// &0 / ' .&: ; ! &// &,( & /3 /&&3 %/ $ . (, &: 9 & . .&/ @ ; H0&( & &: & / & ' /& 0& ; / 0, ' &. /& &% # 8 *' . %& ! ! //0 & . (., 2 & & ( ' .& / ( / . /&:& ' ( $& & '& & ! ..' $ &43 .' & &/< & . /&:& ' ( $& # '& & , & :.' & ./: /&:& ' ( $& # ;&/ ' . .+,, # % / ' . /&:& ' /&: ( &4 ) ! C % & . 3 . : $# 8 ) / ,: %/ $&.& 3 .4$'&' / %/& #.& 5678 3 .4$'&' / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" 0+ (9( !. 2 !, 0+ (9( !. 2 !, 3- 3- : C& & .(& & &. $& : 0, ' &. /& , .&// &0 ( L//0 ' &. /& & 6 0$ 0;(.(+!, ( ! & , ' &. /& * .&//& ( ' ( H&. / & L//0 6K0$ .& . ( $& ( ! &$ L//0 ' &. /& 0++, 6 0$ /&: ( '&0' /& ' / ' &. /& /&: ( '&/ &0 *& / $& M /://& /&: ( (/ &/ * *& / * $& /&: ( '&/ #$/ '& ' &. /& /&: ( '&0' & ' &. # $ %,&4 .&/ & 0 & ( ' 3 &/ .' /&: ( '&0' & ' &. : - &. ) 0 ' &. /& ' '&&. &(, : H / @ &, . & ' C' *' ( $& & ' &. /& < &,( 0' /&: B&$ 0( ( ' &. /& & ( : (, , H4 $&3 ./ $ ( ',./&4 *' /&.4' & '&0' :; +, ,, L//0,&/ . & ' 7 &//0 7 &//0 & &3 &/ /& :;, ( 9 % .'3 ..&&// &/ '&/ $ /&: ( &. ' & 3 .' ( 2 2 % / % /& & &//0 0//0 . ! ((, . ( , 0&//0 .' # 8 /&: ( & / % , 0&//0 % /& & &//0 0//0 ! .&./ / #(.+, C H&$$ . & ' '/.4 )& & / / '&$ :& ' &. /& / & &43 ( $ ( $ )& & H& ' &. /& ' . & ' ' /,'& H& ' &. /& ;., $' #.' $& $&3 .& :$& / & & /.' , H&4 #.' $& ( $ ( & & / .& /: L / & ' ' &. /& , &/ +(.+, ::$ 02 9$& ( ; & 0 $ /& 8 8 /& ' &. /& # I.& .'&& */ . ' &. /& ;+, #/ *' $&3 .&// G& .& & .& $& :& $& G , .4 . & ' $& 2 H , & . $& ' & / & ' ' &. /& ! &4 , &// ( $ '$' ' .& ! H 4 &//0 $& , ' (/0 & ! $& &// &,( & '3 &/ / ! $& 6.& ' &. /& ! $& ! I . ' &. /& , .&// & / & ' &. /& , ' /&( / ! $$ / 43 0&// . ! $',/ 0, ' &. /& & 0& .&// * / .&//& ( ' ( '/ . //& & ' / , $& ( & & .& $ :$& / & &. ! &4 & /& $& / & 4 &. $& 3 .4$'&' / %/& #.& 5678 3 .4$'&' - / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" 0+ (9( !. 2 !, 0+ (9( !. 2 !, 3- 3- ) '&0'3 ..&&// 0& # = ' &. /& .+;(, = ' &. /&3 & ' &' & &$ ' &$ (.!, 8 8 &' & ( & ' ;/'& )&04,' & 0//0,' ! & &' (/&$ %/& )&04,' /& & &//0 0//0 ( ' $' &.& 0' &43 ( $ & )&04,' 3 /3 &/ , ..&&// .' & &4 &' ' /&: # ; )&04,' &//03 &/ (+;!, , ! & &/ . & & &' (/&$ 4# 5 2 & &/ . ) K . & +-, ) K . ! & '3 ' $3 . .+, ! & '3 ' $3 . /&: ( & / ! &4 ++, & @ 3 &// &.& 0' 0 $ &/3 .& . 2 & & $& , ' 2 % / &/ & & / & & ( &' .& & 2 ? !! & 0 /&.0$ /&:& & &' & & ' '&0'3 /&.4' & &/ & #$# ! .' !+, ' &. /&2 &R 0 & ' ; / ,&/ &/(/ ( & 0& 3 ' & / & / , ' (/ $ ( *& # $ ' &. /& , ..&&// # &# ' &. /& +,, &$0 ! / $&' $&/& &/ , ' '& *& 0 $&' $&/& ( .&3 C&/3 % . /&3 C &//3 $&/& '&' & H&. ( // C&' ! $0 , ' & /0 !, ! ',0$ , .&/ (/ & & .&&/ 0 ( & ! 23 &/ & / '& :& ( /& '& & !! / & &/ , ( ' ' ' /&: .4/ ', $' ' &$ & . &/< & % / 2 ..4 . & B&4 ',..4 &4 3 .&// 0' & ' 0 /& $ '/ & & & $& , ' (/0 '& & /K ', G /$ $&/& * ! . & ' 3 ( $ ( & /4 ..4 / /0 /&( (&. H&4 ',..4 . & $ '& & ! &. % 3 .&// /&.4' ?'K,0 . & ' . & ' %! & ' , .&// : & /&.4' # 3 ' & ' &. /& ) C B&4 < &4 < &4 ( , 0 $''& 5 08 & & / $''& & $& ( :& > <8 % # +(, $ '& & $ '& & 3 .4$'&' / %/& #.& 5678 3 .4$'&' " / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" $78 #$ #% % % # 2 G&&// & . & ' (&//$ 0' ' & .&$ ( ' % $ 5&3 ++ D '3 +" 82 ' & &&// .$ . / ' :& % $ /' 3 ' & . (3 ' 9&&/ 6 ( ' :& ( G& 596G82 . ./ & (&// : &( 0 .&$2 ' & ( .&$ G /& (/ ' < ( ' 2 & (//0A H &<& &$ ( <. & 0' ::&/ /4/ ( ' .& &/ (&. . &$2 ' ./ A . 40 ( / & $/ /.&/ . + !D . . '& & 0'.' & .&// : /& /D . 0'.' '&: '0 & & & . ./ ' /& 0 & & & 0 & < (: (0 /.&/D . /: <. 0'.' 0 / . ( , .: 2 H OI /& /P2 &<& /: /4/ : ' ; &$ .&$ ' & ( ( ' .& &/ (&. . &$2 ' ./ A . ./$ ' $' ' &$D . : /& / '& &D . 0' /& & /02 H O&P2 &<& 0' &// /& 0'.' & & &$ : /& / 0'.' & & 42 ' ./ A . 0'.' & & .. (( (0 /.&/2 H 7 &<& . (&// 0' ' H .&$ 0'.' & & ((./ 40 & / /&.2 # 2 G&&// .&. . & ' (&//$ 0' ' G&&// G& / .&$ . &// 5 +"-82 ' & . 0'.' & & .. 0' ' &$ ( - !! ,4/ @ & ( ' ' G&&/ C . + !2 ' .(. .&$& ( . '&: : . ' . ( & ( &<&D ' : & &4 &.. ' 2 G& / . & : & (//0A G& . & .. 0' ' &$ ( - ! !,4/ @ & ( ' G&&/ C 2 G . & .. 0' ' &$ !! !,4/ @ & ( ' G&&/ C 2 G H& 5(/8 && 3 (&//$ ' .&$ G& G 2 # 2 G&&// .&/ . & ' 0'.'3 0'/ (&/ .3 & : / / 0 & '& / . .3 &/ @ &/( $ & G&&// G& / '&:$ . ( : ' 3 / '& ' ' 3 ,4/ @ & ( ' 67 G&&/ C 2 ' <.3 O.&/P $& '&: & ( ' ;BH; (0&2 ' G&&/ & 3 0' ' & .&/ 3 & .& &$& . & # . 3 & 2 3 .4$'&' + / %/& #.& 5678 3 .4$'&' ! / %/& #.& 5678 9: & : /& ;/$ 9: & : /& ;/$ # $ !!" !" # $ !!" !" . /( / 0 /($0 +.$+('$00-' %*-*12! M-. $* M/($* 2M2'4(* M00$+ -$5 !M!$' 1 ++1-'*%'$++5$1$+/1$& 56%'$7/6'$// *+$1$+$*01+-8/$'%'-( .$55$*01+-8+0'(/$''+**1'-(%1-(**18 5 9-++ +$/($* :**'$'$+ 1+:$'0-.' ++0-..-$: +'$+0 +$ +.-'$*56+0 +;' 01 + '$/5'$%:-'*$*1 +*5$'8'4(* <$ '6$*;='$++ 2$5+$*;='$++ 2 -..-"* 2 ' %"* 2 1R+2+0( ?-'@+1 '2-% 2 -0@+8--* '8-'$* *;-1R+-'* -..-!$%:-'* 2 ! /:-'*5$*$ 2 ?$''-: "5$0@A$: ! "5$0@9 0@ 2 ' % 1 +*5 2 1 * 5-&' ='$* 55-:1'/ ! ! $' 1 +*5 ' % 4(8- 5 -..-B*01 " ! -..-9-(+;$' ! <-%: ! (8*2-'%*;9;-* # ++ ! $% &'()$'*'+#* ! " # ++( ,-&./' , # ' %"(**'0( $ -..-" 'R+;8--* '8- 5 % ('5-0@ $# 9(%:-'* ! .--*1 $' " ' 0@56#**(0 % $%% ! 0*9$6: ! ! 5-&' 5 $''-* ++ ! 1 * 5-&' "' +*56 ; -%( ! ;6$ +6 % ! .-*16 <$'!(+1 ' # 2 <$:*1-' @!(+1 ! 2 -%!-+ $ - *!(+1 ' "'$./5 $ -8*!(+1 ' 2 5' -..-25$/$ 2 (*;5$& '$+;/ 55 & ! .--*1 $' " 1 +8 5 +.$ 56+0 +;--'+. ; .'-&(*'$5%'$++5$C: *1-00$+ -$5$*01+ 9$-:"(**'0( $ -8.$'+16D$.%'$++5$ -5*R+;8--* %' .-6 ! #++' $':-'* $ ! ?-'@+1 '2-% 2$5+$*;='$++ 2 1 +8 50-.' +++. ; .'-&(*'$5%'$++5$: *1$.-'$*56 &'+'$%-8 ' %"* 2 %'$+++$1'/+0 +$-00$+ -$5$*01+-8+0'(/$$.$'$+ .-*16 2 -..-B$5' $ " -..-!$%:-'* ! .-*16 ! /:-'*5$*$ ! ' %"* 2 ?$''-: ! ?-'@+1 '2-% 2 "5$0@9 0@ ! 2$5+$*;='$++ 2 $' 1 +*5 :*B'$5='$++ # ' %"(**'0( $ ' $5!6;='$++ % "' +*56 ; -%( ! "'-:"* ! $. - ! "5$0@"* 1 * $. - ! -8*!(+1 ' ! ' % 4(8- 5 ! -..-25$/$ -&+;8--* '$R+;/ 55 & ! ' % 1 +*5 $% &'()$'*'+#* $%E &'()$'*'+#* ! " # ++( ,-&./' , ! " # ++( ,-&./' , # # 1 +8 51$+$&$' +*'(0*('$0-.' +++1-'*$*$55%'$++5$$+:55$++0'(/ ' %"(**'0( $ 1%'$++5$ +.-'$*56+0 +;' 01 *1:+*/(*/0-.+-. $*/68$5+-$*; -..-!$%:-'* ! %'$++*-*1$+* 1 * 5-&' ! -..-" 'R+;8--* '8- 5 % 9$-:B*015 % % ?-'@+1 '2-% 2 .--*1 $' " 2$5+$*;='$++ "'-$;5$&-0@ $# ! -0@+8--* 2 -..-B*01 " ! -8*!(+1 ' "5$0@A$: ! -..-!$%:-'* ' 0@56#**(0 % $%% ! -..-**5 ( -..-**5 ( ! ' % 1 +*5 <-%: ! -..-" 'R+;8--* '8- 5 % 2 5" : ! ='$* 55-:1'/ ! #++' * *01:-'* ! <-%: -..-B*01 " 4($';+*$5@ 55-:1'/ ! ! 1 +8 5 +-. $*/60-$'+%'$+++$ +%'$556+0 +;--' <-:&'C *-+ %(* 1$&$8:+0 +*1$*$'-*8-( *1-*1'8 5+-+ * -..-25$/$ ('5-0@ $# -0@+8--* <$ '6 $' " 2 2$5+$*;='$++ ' $5!6;='$++ % "'$./5 $ ' %"* (8*B*01 " .-*16 " **'+:* 1 * 5-&' -..-**5 ( 2 "'-$;5$&-0@ $# 2 9(%:-'* ' % 1 +*5 2 2 5!-+ $ "5$0@9 0@ <%-(:-'* <-%: ='$*'5$*$ ! 5-&' 1 ++. ;.$*('/'-$5$&:--5$1$+$'$%-8$* &*'+0 +$$&$' $%;+*'(0*(' &'$505$' %+:1 01$'-. $*/6/'$0@$$;:-- + 2 5" : '+* 5$0+ 1+0 +5 +*$'*1-+'+*$**1* .-8*1+('&6 (56 (*(.<$:@/ * % ! "5(/55 ) $' .'-+ :''0-' +' % $% &'()$'*'+#* $%F &'()$'*'+#* ! " # ++( ,-&./' , ! " # ++( ,-&./' , # # $@ * 2 "01 2 <-'/$. 5&'" '01 + 2 <$75 55-: # + 2 <-556 ,# - <$:*1-' 2 +1 # # 60$.-' + --"'-. + ! 2$5+"'-. + 2$5+$*;='$++ ! (8*<$ ';='$++ ! 01$*'R+ %1*+1$ ! ---0@ $# &$' ! <-6+(0@5 % 5:-'* % ! "'$./5 $ 2 "'$0@ - <%-(:-'* ! 5$&'+ & ! -- ('% ! ! <%" : ++ ! $%G &'()$'*'+#* ! " # ++( ,-&./' , # 1 2( ! " # $ % & ! " ' ( ) * & +! , !" $! + ! + , ! -.+ / 0 1 2 -3.+ 34 3 - + - + ( ' + + 5 =!& 0, =!& H , H :; :; :; :; ! 0 ' % 1" %& % " %" E @ * @ $ $"#@ " 2" % + " %" E @ * @ $ $"#@ " & 2" %1 & +" %"2 E @ * @@ 00 "B @ " + 1" %2 + 2" " @ B "9 % " 2 0" %0 % &" &" # ! @ $ A " ' 1 0"2 && % +" &" E ! !$ " ' 0 0" % % 1" &" E @ F " ' C 1" && 1" " @ " @@$ " ' 1" % &" %"2 E @ $ $ $ $"B " % 2" %2 % %" " # ! $ $ $ $" ' %% ! 2" %+ % &" %" # @ = @ A $ " % $ 2" %C % +" " E ! ! @ " %& +" %+ % " "2 E B@ $ " ' %+ %+" % & % " " : @ @ $$ " ! @$ " =!& 0, =!& H , H :; :; :; :; ! 0 ' %2 2" %C " "2 E B@" %1 2" % " " E B@"' @ " %0 0" %2 " " E ! @ " $ $ " %C $ %2" % +" %"2 E @ F ! " $$ $ $" % ! " " " : ' 0" %0 2 +" %"2 E ! @ @ " I @ $ " @! " 7 @ ! " $ $ " " ! @ ! % %C" % + % " " M @ $ " %" C+ % % " %" M @ M@ @ ! "9 @ $" & %C" 12 % C" %" @ 8@ $"F ! " ' + % " % 2" %" E ! ;@ " 2 " + % 1" "2 # ! ;@ " ' 1 2" %1 +" %"2 E B@ " $ ! "' @" $ $" 0 0" 0 % 1" &" E ! A !@ " $ " C % " 0 % % " %" E ;@ $ A " %" 2C % % " &"+ @ B @ "# " & " 2C %%" 2"2 @ F @ " !$@! $$ @@ " &% 2" % +" %" # @"@ " & C" %C &" " E ! < @! $$ $ $" ' && C" +" +" @ "'$$" "= ! @ " ' &+ C" % &" "2 9 $!" !$ " ' &2 " ++ & +" %" ! @ $ @ @ " ' &1 " % % &" %" ! @ " &0 C" 2 + 2" %" @ $ $ $" &C 1"2 & & 2" "2 ! @ " !$ " & %0" 2& % 2" " @ # " + 1" + % " %" E B@! " +% %C" 2C % C" %" M @ # " ' + %2" 1& % 0" &" @ # " ' +& 1" %2 &" &" # @! " ++ +" %+ %" %"2 # @! "# " +2 1" ++ % +" " E @ # $ @"F ! " +1 2" & % &" &" E @ ! "B " +0 @ 1" %2 % "2 &" E @ F "# ! = " +C @ 1" % +" &" E @ F "# ! = " + @ 1" 2 % +" &" E @ F "# ! = " ' 2 @ 1" %2 % +" +" E @ F "# ! = " ' 2% @ 1" 2 % +" +" E @ F "# ! = " 2 @ 1" 2 % +" +" E @ F "# ! = " ' . A A ? ? )0= /0)*,,0) .9=B/. / * $ ,&& # '( Pinewood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inewood Studios Ltd Pinewood Survey Area Boundary '3 *'6+2 B@#! * ,! =* 9 & = 8 ,! % * & = 8 ,!( =* '! & = 8 456 0 6 0 +#78*99: ;:#9 6%+8#<68 68 -<87:#=8 # ;8 &6<87:#=8 6<87:#>% 6<&6% "%%B#FB* ° Survey Area : # !8! 343 1! 343 1!1 74 !8! !! 9 !8! !! 7473 8!! , 73 8!! 7 ! ((.4(.4, 5" # 5 # 12! 33! 0 ( ( +( ( ! "#$ %&'()(*+ +, -%&'()(*,.( / Pinewood Studios Ltd Pinewood ! "# #$ % & #'# '3 ° Survey Area : # !8! 343 1! 343 1!1 74 !8! !! 9 !8! !! 7473 8!! 73 8!! 7 ! ((.4(.4, 5" # 5 # 12! 33! 0 ( (+(, ! "#$ %&'()(*+ +, -%&'()(*,.( / Pinewood Studios Lt Pinewood ! "# #$ % & #'# '3 ° Survey Area : # !8! 343 1! 343 1!1 74 !8! !! 9 !8! !! 7473 8!! 73 8!! 7 ! ((.4(.4, 5" # 5 # 12! 33! 0 (, /( .( ! "#$ %&'()(*+ +, -%&'()(*,.( / Pinewood Studios Ltd Pinewood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urvey Area Trees with bat roosting potential Building with bat roosting potential Pipistrelle activity Myotis activity Serotine activity F1 2008-09-11 HW AB NH Issue Date By Chkd Appd Metres 0204010 13 Fitzroy Street London W1T 4BQ Tel: +44 (0)20 7636 1531 12 Fax: +44 (0)20 7580 3924 11 Client 3 Pinewood Studios Ltd 1 2 9 Job Title 10 5 6 7 8 Pinewood 4 Drawing Title Five Points Roundabout Bat Survey Scale at A4 1:977 Drawing Status For Issue Job No Drawing No Issue 207042-09 Figure 1 F1 © Arup Legend Survey Area Trees with bat roosting potential Building with bat roosting potential Pipistrelle activity Myotis activity Serotine activity 13 14 F1 2008-09-11 HW AB NH 15 Issue Date By Chkd Appd 16 17 Metres 18 045 90 180 19 13 Fitzroy Street London W1T 4BQ Tel: +44 (0)20 7636 1531 20 Fax: +44 (0)20 7580 3924 21 22 Client Pinewood Studios Ltd Job Title 29 Pinewood 27 Drawing Title 26 Sevenhills Road Widening Bat Survey 25 24 Scale at A4 1:4,532 Drawing Status 23 For Issue Job No Drawing No Issue 207042-09 Figure 2 F1 © Arup Legend Survey Area Trees with bat roosting potential 36 Building with 37 bat roosting potential 34 Pipistrelle 3233 35 activity Myotis activity 22 30 31 Serotine activity 29 27 28 26 F1 2008-09-30 HW AB NH 25 Issue Date By Chkd Appd Metres 24 030 60 120 23 13 Fitzroy Street London W1T 4BQ Tel: +44 (0)20 7636 1531 Fax: +44 (0)20 7580 3924 Client Pinewood Studios Ltd Job Title Pinewood Drawing Title Sevenhills Road Junction Site Scale at A4 1:3,132 Drawing Status For Issue Job No Drawing No Issue 207042-09 Figure 3 F1 © Arup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