Mineral and Waste Sites Assessment Minerals and Waste Sites Local Plan

Home , Appleton Lower Common, Balscote, Chimney Meadows, Cuttle Brook, Ewelme Watercress Beds, Harpsden Wood

For Oxfordshire County Council

Technical Supporting Document: Adams Hendry Consulting Ltd.

January 2020 Title Mineral and Waste Sites Assessment

Client Oxfordshire County Council

Project Number OCC/1592

Status V3 Final

Report Number OCC/1592/V306012020

Adams Hendry Consulting Ltd. Sheridan House, 40 – 43 Jewry Street, Winchester, SO23 8RY T 01962 877414 E [email protected] www.adamshendry.co.uk

Author Name: Jane Parker Date: 6th January 2020

Approved by: Emma Barnett Date: 6th January 2020

Certified to ISO9001 Standard

ISO 9001 Registration Number Q10324

Registered Office: Sheridan House, 40 – 43 Jewry Street, Winchester, SO23 8RY Registered in England No. 3804753 VAT Registration No. 807 9759 79 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Final

Contents

Contents ...... 3 List of tables ...... 6 1 Introduction ...... 7 2 Stage 3a: Initial Screening ...... 9 3 Stage 3b: Detailed Technical Assessment ...... 21 4 Stage 4: Identification of and Consultation on Preferred Options ...... 22 Appendix 1 Stage 3a Eliminated Sites ...... 23 Site 005 – Playhatch Quarry, Playhatch ...... 24 Site 013: Ewelme No. 2 Site, Goulds Grove, Ewelme ...... 28 Site 030 Shipton on Cherwell Quarry, Kidlington ...... 32 Site 138 Woodside, Ewelme ...... 36 Site 152 Ewelme No. 1 Ewelme ...... 40 Site 180 Elmwood Farm, Black Bourton ...... 44 Site 217 Culham No. 4 Site, Culham Science Centre ...... 48 Site 222 – Land to the north of Wroxton Fields Quarry, Wroxton ...... 52 Site 225 – Cedars Storage, Benson ...... 56 Site 248 Thrupp Lane, Radley ...... 60 Site 249A – High Cogges Farm, Witney ...... 64 Site 250 – Broughton Poggs Business Park ...... 68 Site 262 - Lower Heath Farm, Cottisford ...... 72 Site 265 – Woodeaton Quarry, Islip ...... 76 Site 277 – Land adjacent the B480, Chalgrove ...... 80 Site 280 – Oxford Shooting School, Enstone Airfield ...... 84 Site 281 – Faringdon Quarry, Faringdon ...... 88 Site 286 – Wally Corner, Berinsfield ...... 92 Site 288 – Brize Norton Road, Minster Lovell ...... 96 Site CR-03 – Southern Extension to Rollright Quarry ...... 100 Site CR-08 – Castle Barn Quarry ...... 104 Site CR-18 – Shipton-on-Cherwell Quarry ...... 108 Site SG-03 – Land adjacent to Benson Marina ...... 112 Site SG-04 – Land at Mead Farm ...... 116 Site SG-05 – Land to the East of Cassington Quarry ...... 121 Site SG-12 – Land South of Chazey Wood ...... 126 Site SG-13 – Land at Shillingford ...... 131 Site SG-15 – Dairy Farm (including SG-58 and SG-58a) ...... 136 Site SG-16 – Land at Stonehouse Farm ...... 141 Site SG-36 – Land at Friars Farm ...... 146 Site SG-37 – Land at Grandpont and South Hinksey ...... 151

Site SG-41 – North of Lower Radley ...... 156 SG-61 – Mains Motors ...... 161 SS-17 – Land north and south of A420 near Fyfield and Tubney ...... 165 Appendix 2 Stage 3b Detailed Site Assessments ...... 169 Site 002 – Prospect Farm, Chilton ...... 170 Site 003 – Dix Pit, Stanton Harcourt ...... 177 Site 008 – New Wintles Farm, Eynsham ...... 184 Site 009 – Worton Farm, Yarnton ...... 191 Site 010 – Sutton Courtenay Landfill (Areas 2 & 3), Appleford Sidings ...... 198 Site 011 – Finmere Quarry, Banbury Road, Finmere ...... 207 Site 018 – Holloway Farm, Milton Common, Wheatley ...... 215 Site 026 – Whitehill Quarry, Burford ...... 222 Site 103 – Land at Lakeside Industrial Estate, Standlake ...... 230 Site 224 – Ambrose Quarry, Ewelme ...... 237 Site 229 – Shellingford Quarry, Stanford in the Vale ...... 244 Site 236 – Sheehan Recycled Aggregates Plant (Dix Pit Complex), Stanton Harcourt ... 252 Site 245 – Challow Marsh Farm, West Challow ...... 258 Site 249B – High Cogges Farm, Witney ...... 264 Site 261 – The Marshes, Knightsbridge Farm, Yarnton ...... 270 Site 274 – Moorend Lane Farm, Thame ...... 277 Site 276 – Oday Hill, Sutton Wick ...... 283 Site 278 – Land off the B4100, Baynards Green ...... 289 Site 279 – Land rear of Ford Dealership, Rycote Lane, Thame ...... 296 Site 283 – Hatford Quarry Extension, Stanford in the Vale ...... 302 Site 285 – (Magnox) Harwell Site, Harwell Campus ...... 308 Site 287 – Ardley Fields ...... 315 Site 289 – Overthorpe Industrial Estate, Banbury ...... 323 Site 290 – Culham Science Centre ...... 330 Site CR-07 – Adjacent to Whitehill Quarry ...... 337 Site CR-10 – Burford Quarry SW Extension ...... 344 Site CR-13 – Dewars Farm Quarry East Extension ...... 351 Site CR-15 – Land off the B4100, Baynards Green ...... 358 Site CR-19 – Dewars Farm Quarry South Extension ...... 364 Site SG-08 – Lower Road, Church Hanborough ...... 371 Site SG-09 & SG-59 – Land north of Drayton St Leonard and Berinsfield and land at Stadhampton ...... 380 Site SG-11 & SG-65 – Land situated Northeast of Sonning Eye (Caversham phases ‘D’ & ‘E’) 387 Site SG-17 – Land at Culham ...... 396 Site SG-18 – Land near Standlake ...... 404 Site SG-20 – Land between Eynsham & Cassington ...... 411 Site SG-20a – Land between Eynsham & Cassington ...... 418 Site SG-20b – Land between Eynsham & Cassington ...... 426

Site SG-23 – Windrush North, Gill Mill ...... 434 Site SG-27 – Vicarage Pit, Cogges Lane ...... 442 Site SG-29 – Sutton Farm, Sutton ...... 450 Site SG-42 – Nuneham Courtenay ...... 458 Site SG-60 – White Cross Farm ...... 465 Site SG-62 – Appleford ...... 472 Site SG-63 – Finmere Quarry ...... 481 Site SG-67 – Sutton Wick Quarry ...... 489 Site SS-03 & CR-17 – Hatford Quarry South Extension ...... 497 Site SS-04 – Land at Pinewoods Road ...... 504 Site SS-05 – Land at Kingston Bagpuize ...... 510 Site SS-07 & CR-24 – Home Farm, Shellingford ...... 516 Site SS-08 & CR-16 – Shellingford Quarry (Western Extension) ...... 522 Site SS-12 & CR-12 – Land at Chinham Farm (Chinham Hill) ...... 529 Site SS-15 & CR-11 – Hatford Quarry North Extension ...... 536 Site SS-16 & CR-21 – Hatford Quarry Stanford Extension ...... 543 Site SS-18 & CR-22 – Hatford Quarry West Extension ...... 549 Site SS-19 & CR-23 – Home Farm, Carswell ...... 555

Table 1 Long List of Nominated Sites ...... 9 Table 2 Traffic Light Assessment Methodology ...... 14 Table 3: Site Assessment Criteria ...... 15 Table 4: Outcome of Stage 3a Initial Screening ...... 16

Purpose of this report

The Oxfordshire Minerals and Waste Core Strategy (Part 1 of the Development Plan) was adopted by the County Council in September 2017. It sets out the vision, objectives, spatial planning strategy and policies for meeting the requirements for the supply of minerals and the management of waste in Oxfordshire over the period to 2031,

Oxfordshire County Council is currently preparing the Oxfordshire Minerals and Waste Local Plan: Part 2 – Site Allocation (Sites Plan). The main purpose of this plan is to allocate sites for minerals and waste development within the policy parameters set by the Core Strategy, to provide for the development needs established in the Core Strategy for the period to 2031.

The purpose of this report is to document the site assessment methodology used to guide the selection process for the allocation of sites to meet the identified need for minerals and waste development.

Background

To provide a consistent basis for the process of selecting sites for allocation, a draft Site Assessment Methodology was prepared and consulted on in January 2018 alongside the Draft Sustainability Scoping Report. An amended Site Assessment Methodology and Sustainability Scoping Report was then published for further consultation alongside the Issues and Options Report in August 2018.

The Site Assessment Methodology has followed a staged approach.

Stage 1a: Initial ‘Call for Sites and Stage 1b: Identify a Long List of Sites

A ‘call for sites’ to potentially meet the County’s requirements for minerals and waste development over the plan period to 2031 has been made at various stages in the preparation of the Minerals and Waste Local Plan both for the Part 1: Core Strategy and the emerging Part 2: Sites Plan. A call for sites to identify a long list of sites for inclusion in the Issue and Options report was made in 2015 and again in January 2018 as part of a six-week consultation on the Proposed Site Assessment Methodology. The Council also included sites on the long list that were put forward as part of previous call for sites back in 2006 and 2008 unless it had been notified that they were no longer available.

Stage 2: Consultation on the Issues and Options

Consultation on the Issues and Options, which included a further call for sites, was carried out in August 2018. This led to a long list of nominated sites being drawn up for assessment at stage 3a as discussed in Section 2.

Stage 3a Initial Screening and Stage 3b Detailed Technical Assessment

This report focuses on stage 3a and stage 3b of the site assessment process. As part of stage 3a, each site was subject to an initial screening assessment to identify any key

constraints that could potentially preclude the site from being allocated in the Sites Plan. All sites that were not screened out under stage 3a, were then subject to a detailed technical assessment as part of stage 3b.

Stage 4: Identification of and Consultation on Preferred Options

Based on this technical assessment, Oxfordshire County Council will identify reasonable alternative sites that are considered to best meet the identified requirement for minerals provision and waste management in the Core Strategy as set out in Policies M2 and W3 of the Core Strategy.

Report Content

The structure and content of this report is as follows: • Section 2: Stage 3a Initial Screening • Section 3: Stage 3b Detailed Technical Assessment • Stage 4: Identification of and Consultation on Preferred Options

Stage 3a: Assessment Methodology

The ‘Long List’ of Sites

Since the Issues and Options consultation, a number of sites have been withdrawn by site nominators or have secured planning consent and a number of new site nominations have been received.

The long list of sites assessed at Stage 3a is set out below in Table 1 comprising: • 44 sites nominated for potential waste management uses; • 46 sites nominated for potential mineral extraction; - 27 Sand and Gravel; - 8 Soft Sand and Crushed Rock Sites; - 3 Soft Sand; and - 8 Crushed Rock. -

Table 1 Long List of Nominated Sites

Site Ref Site Name Status WASTE SITES Long Site of Nominated Waste Sites for Assessment at Stage 3a Included in Issues and Options 2 Prospect Farm, Chilton Consultation August 2018 Included in Issues and Options 3 Dix Pit (Area 2), Stanton Harcourt Consultation August 2018 Included in Issues and Options 5 Playhatch Quarry, Playhatch Consultation August 2018 Included in Issues and Options 8 New Wintles Farm, Eynsham Consultation August 2018 Included in Issues and Options 9 Worton Farm Areas C&D, Yarnton Consultation August 2018 (Area 3) Sutton Courtenay Landfill Included in Issues and Options 10 Area 3, Sutton Courtenay/Appleford Consultation August 2018 Included in Issues and Options 11 Finmere Quarry Consultation August 2018 Included in Issues and Options 13 Ewelme No.2 Site, Goulds Gove Consultation August 2018 Holloway Farm, Waterstock/Milton Included in Issues and Options 18 Common Consultation August 2018 Shipton on Cherwell Quarry, Included in Issues and Options 30 Kidlington Consultation August 2018 Included in Issues and Options 26 Whitehill Quarry Consultation August 2018

Lakeside Industrial Estate, Included in Issues and Options 103 Standlake Consultation August 2018 Woodside, Old Henley Road, Included in Issues and Options 138 Ewelme Consultation August 2018 Included in Issues and Options 152 Ewelme No.1 Site Consultation August 2018 Included in Issues and Options 180 Elmwood Farm, Black Bourton Consultation August 2018 Culham No.4 Site, Culham Science Included in Issues and Options 217 Centre Consultation August 2018 Land north of Wroxton Fields Included in Issues and Options 222 Quarry, Wroxton Consultation August 2018 Included in Issues and Options 224 Ambrose Quarry, Ewelme Consultation August 2018 Included in Issues and Options 225 Cedars Storage, Benson Consultation August 2018 Shellingford Quarry, Included in Issues and Options 229 Shellingford/Staford in the Vale Consultation August 2018 Sheehan Recycled Aggregates Included in Issues and Options 236 Plant, Dix Pit Complex Consultation August 2018 Included in Issues and Options 245 Challow Marsh Farm, West Challow Consultation August 2018 Included in Issues and Options 248 Thrupp Lane, Radley Consultation August 2018 Included in Issues and Options 249A High Cogges Farm, Witney Consultation August 2018 Included in Issues and Options 249B High Cogges Farm, Witney Consultation August 2018 Included in Issues and Options 250 Broughton Poggs Business Park Consultation August 2018 The Marshes, Knightsbridge Farm, Included in Issues and Options 261 Yarnton Consultation August 2018 Included in Issues and Options 262 Lower Heath Farm, Cottisford Consultation August 2018 Included in Issues and Options 265 Woodeaton Quarry Consultation August 2018 Included in Issues and Options 274 Moorend Lane Farm Consultation August 2018 Included in Issues and Options 276 Oday Hill, Sutton Wick Consultation August 2018 Included in Issues and Options 277 Land adjacent the B480, Chalgrove Consultation August 2018 Land off the B4100, Baynards Included in Issues and Options 278 Green, Ardley/Fritwell Consultation August 2018 Rear of Ford Dealership, Ryecote Included in Issues and Options 279 Lane, Thame Consultation August 2018 Oxford Shooting School, Enstone Included in Issues and Options 280 Airfield Consultation August 2018 Farringdon Quarry, Farringdon/Little Included in Issues and Options 281 Coxwell Consultation August 2018 Hatford Quarry Stanford Extension, Included in Issues and Options 283 Stanford in the Vale Consultation August 2018 (Magnox) Harwell Site, Harwell Included in Issues and Options 285 Campus Consultation August 2018

Included in Issues and Options 286 Wally Corner, Berinsfield Consultation August 2018 Site nominated since the Issues and 287 Ardley Fields Options Consultation August 2018 Site nominated since the Issues and 288 Brize Norton Road, Minster Lovell Options Consultation August 2018 Overthorpe Industrial Estate, Site nominated since the Issues and 289 Banbury Options Consultation August 2018 Site nominated since the Issues and 290 Culham Science Centre Options Consultation August 2018 Nominated Waste Sites Not Proceeding for Assessment at Stage 3a Alkerton Landfill and Civic Amenity Site Withdrawn by site operator 23 Site, Alkerton Site Withdrawn by site operator 226 Dewars Farm Site Withdrawn by site operator 230 Chinham Farm, Stanford in the Vale This is an existing strategic waste management site that is already 232 Banbury Sewage Treatment Works safeguarded for waste uses in the Core Strategy. This is an existing strategic waste management site that is already 233 Witney Sewage Treatment Works safeguarded for waste uses in the Core Strategy. This is an existing strategic waste management site that is already 234 Didcot Sewage Treatment Works safeguarded for waste uses in the Core Strategy. Land at Field Barn Farm, North of Site Withdrawn by site operator 282 A417, Ardington, Wantage MINERAL SITES

SHARP SAND AND GRAVEL

Long Site of Sites for Assessment at Stage 3a Included in Issues and Options SG-03 Land adjacent to Benson Marina Consultation August 2018 Included in Issues and Options SG-04 Land at Mead Farm Consultation August 2018 Land to the East of Cassington Included in Issues and Options SG-05 Quarry Consultation August 2018 Included in Issues and Options SG-08 Lower Road, Church Hanborough Consultation August 2018 Land north of Drayton St Leonard Included in Issues and Options SG-09 & SG- and Berinsfield and land at Consultation August 2018 59 Stadhampton SG-11 & SG- Land situated Northeast of Sonning Included in Issues and Options 65 Eye (Caversham phases ‘D’ & ‘E’) Consultation August 2018 Included in Issues and Options SG-12 Land South of Chazey Wood Consultation August 2018 Included in Issues and Options SG-13 Land at Shillingford Consultation August 2018

SG-15 (incl Included in Issues and Options SG-58 & SG- Dairy Farm Consultation August 2018 58a) Included in Issues and Options SG-16 Land at Stonehouse Farm Consultation August 2018 Included in Issues and Options SG-17 Land at Culham Consultation August 2018 Included in Issues and Options SG-18 Land near Standlake Consultation August 2018 Land between Eynsham & Included in Issues and Options SG-20 Cassington Consultation August 2018 Land between Eynsham & Included in Issues and Options SG-20a Cassington Consultation August 2018 Land between Eynsham & Included in Issues and Options SG-20b Cassington Consultation August 2018 Included in Issues and Options SG-23 Windrush North, Gill Mill Consultation August 2018 Included in Issues and Options SG-27 Vicarage Pit Cogges Lane Consultation August 2018 Included in Issues and Options SG-29 Sutton Farm, Sutton Consultation August 2018 Included in Issues and Options SG-36 Land at Friars Farm Consultation August 2018 Land at Grandpont and South Included in Issues and Options SG-37 Hinksey Consultation August 2018 Included in Issues and Options SG-41 North of Lower Radley Consultation August 2018 Included in Issues and Options SG-42 Nuneham Courtenay Consultation August 2018 Included in Issues and Options SG-60 White Cross Farm Consultation August 2018 Included in Issues and Options SG-61 Mains Motors Consultation August 2018 Included in Issues and Options SG-62 Appleford Consultation August 2018 Included in Issues and Options SG-63 Finmere Quarry Consultation August 2018 Included in Issues and Options SG-67 Sutton Wick Quarry Consultation August 2018 Sites Not Proceeding for Assessment at Stage 3a Granted Planning Permission SG-14 Stonehenge Farm Granted Planning Permission SG-19 Bridge Farm Site Withdrawn SG-28 Guy Lakes North Site Withdrawn SG-30 Home Farm, Brighthampton Site Withdrawn SG-31 Land East of Sutton Land South of Wallingford, New Granted Planning Permission SG- 33 Barn Farm

CRUSHED ROCK (CR) SITES

Long Site of Sites for Assessment at Stage 3a Southern Extension to Rollright Included in Issues and Options CR-03 Quarry Consultation August 2018 Included in Issues and Options CR-07 Adjacent to Whitehill Quarry Consultation August 2018 Included in Issues and Options CR-08 Castle Barn Quarry Consultation August 2018 Included in Issues and Options CR-10 Burford Quarry SW Extension Consultation August 2018 Included in Issues and Options CR-13 Dewars Farm Quarry East Extension Consultation August 2018 Included in Issues and Options CR-15 Land off the B4100, Baynards Green Consultation August 2018 Included in Issues and Options CR-18 Shipton-on-Cherwell Quarry Consultation August 2018 Dewars Farm Quarry South Included in Issues and Options CR-19 Extension Consultation August 2018 Sites Not Proceeding for Assessment at Stage 3a Great Tew Estate Quarry Granted Planning Permission CR-09 Land at Burford Road, Brize Norton Site Withdrawn CR-20

SOFT SAND (SS) AND CRUSHED ROCK (CR) SITES

SS-03 and Included in Issues and Options Hatford Quarry South Extension CR-17 Consultation August 2018 SS-07 and Included in Issues and Options Home Farm, Shellingford CR-24 Consultation August 2018 SS-08 and Shellingford Quarry (Western Included in Issues and Options CR-16 Extension) Consultation August 2018 SS-12 and Land at Chinham Farm, Chinham Included in Issues and Options CR-12 Hill Consultation August 2018 SS-15 and Included in Issues and Options Hatford Quarry North Extension CR-11 Consultation August 2018 SS-16 and Included in Issues and Options Hatford Quarry Stanford Extension CR-21 Consultation August 2018 SS-18 and Site nominated since the Issues and Hatford Quarry West Extension CR-22 Options Consultation August 2018 SS-19 and Site nominated since the Issues and Home Farm, Carswell Quarry CR-23 Options Consultation August 2018 SOFT SAND (SS) SITES Included in Issues and Options SS-04 Land at Pinewood Road Consultation August 2018 Included in Issues and Options SS-05 Land at Kingston Bagpuize Consultation August 2018 Land north and south of A420 near Included in Issues and Options SS-17 Fyfield and Tubney Consultation August 2018

PULVERISED FUEL ASH (PFA)

Site Not Proceeding for Assessment at Stage 3a No identified requirement for PFA in the PFA-01 Land at Thrupp Lane, Radley Oxfordshire Core Strategy

CLAY

Site Not Proceeding for Assessment at Stage 3b No identified requirement for clay in the Oxfordshire Core Strategy (only relates to a small area of the site nomination. The SG-63 Finmere Quarry remainder site nominated for sand and gravel extraction has proceeded for assessment.

Each site on the long list was subject to an ‘initial screening’ exercise to rule out any sites that have overriding constraints such that they would not be suitable for inclusion in the Sites Plan. This was a desktop exercise, using data primarily available on OCC’s Geographic Information System (GIS) or provided by site nominees.

The initial screening exercise utilised a traffic-light system of assessment, based on a Red, Amber, Green (RAG) methodology. The Site Assessment Methodology (August 2018) had envisaged that the RAG assessment would include; Red, Red-Amber, Amber, Amber- Green, and Green. However, in practice, the Red Amber, Amber and Amber Green categories have been combined into an Amber only category as it was considered that there was a risk in making a finer judgement within the Amber range given the level of information available through the desktop exercise and the variable quantity and quality of information provided by site nominees.

Table 1 outlines the values that have been assigned to these categories.

Table 2 Traffic Light Assessment Methodology

Sensitivity Score Description

RED There is a very substantial negative effect.

AMBER There is a negative effect or issue which may be able to be adequately addressed with mitigation.

GREEN There are no effects or issues of significance that require mitigation.

The assessment categories and explanation of the sensitivity score are set out in Table 3.

Table 3: Site Assessment Criteria

Site Assessment Categories Assessment

Compliance with Minerals Strategy – Whether the site is within either a MSRA and/or Strategic Resource Areas (Policy M3) is an extension to an existing site.

For relevant mineral sites nominations only

Compliance with Waste Strategy – Whether the site is an appropriate strategic or non strategic waste facility for its location and For relevant waste management sites the proximity of the site to the Oxfordshire Lorry nominations only Route.

District Local Plan Allocation Whether the site within an area allocated in a District Local Plan for development.

Biodiversity and Geodiversity (Policy C7) Likely effect on International/ European sites (SAC, SPA and Ramsar), national designations (SSSI or National Nature Reserves), Local Nature Reserves, Local Wildlife Site or a Priority Habitat Creation or Restoration Area or an irreplaceable habitat (Ancient Woodlands).

Landscape / Visual (Policy C8) Likely effect on an AONB

Water Environment and Flooding (Policy Likely effect on Source Protection Zones (SPZ) C3 and Policy C4) 1, 2 or 3, Principal and Secondary Aquifers and Flood Zones.

Air quality (Policy C5) Likely effect on Air Quality Management Areas (AQMA)

Soil resources Policy C6) Likely effect on Agricultural Land Classification (ALC) Grade 1, 2, 3 or 4.

Historic Environment (Policy C9) Likely effect on designated heritage assets or non-designated heritage asset (equivalent to a Scheduled Ancient Monument (SAM).

Transport (including access) (Policy C10) Access to the SRN and/or potential access to a rail head or navigable waterway. Strategic Road Network (SRN) is as

identified in the Core Strategy (Figure 13)

Public Rights of Way (Policy C11) Likely effect on PRoW network

Health and Amenity (Policy C5) Likely effect on residential/sensitive development

Green Belt (Policy C12) Appropriate or inappropriate development in the Green Belt

Airport Safeguarding (Policy M10) Whether the site is or within an Airport Safeguarding Zone

The proximity of each site to other existing or nominated operations (minerals and waste) was also recorded to identify any potential cumulative impacts.

Outcome of Stage 3a: Initial Screening

Those sites that were considered potentially suitable for inclusion in the Sites Plan following the initial screening exercise were taken forward for further detailed technical assessment. The outcome of the initial screening stage is set out in Table 4.

Table 4: Outcome of Stage 3a Initial Screening Stage 3a- High Level Site Ref Site Name Assessment Outcomes WASTE SITES Sites Proceeding to Stage 3b: Detailed Technical Assessment

2 Prospect Farm, Chilton

3 Dix Pit (Area 2), Stanton Harcourt

8 New Wintles Farm, Eynsham

9 Worton Farm Areas C&D, Yarnton (Area 3) Sutton Courtenay Landfill Area 3, 10 Sutton Courtenay/Appleford 11 Finmere Quarry

18 Holloway Farm, Waterstock/Milton Common

26 Whitehill Quarry

103 Lakeside Industrial Estate, Standlake

224 Ambrose Quarry, Ewelme Shellingford Quarry, Shellingford/Staford in the 229 Vale

Sheehan Recycled Aggregates Plant, Dix Pit 236 Complex 245 Challow Marsh Farm, West Challow

249B High Cogges Farm, Witney

261 The Marshes, Knightsbridge Farm, Yarnton

274 Moorend Lane Farm

276 Oday Hill, Sutton Wick Land off the B4100, Baynards Green, 278 Ardley/Fritwell 279 Rear of Ford Dealership, Ryecote Lane, Thame Hatford Quarry Stanford Extension, Stanford in 283 the Vale 285 (Magnox) Harwell Site, Harwell Campus

287 Ardley Fields

289 Overthorpe Industrial Estate, Banbury

290 Culham Science Centre

Sites Eliminated

5 Playhatch Quarry, Playhatch

13 Ewelme No.2 Site, Goulds Gove

30 Shipton on Cherwell Quarry, Kidlington

138 Woodside, Old Henley Road, Ewelme

152 Ewelme No.1 Site

180 Elmwood Farm, Black Bourton

217 Culham No.4 Site, Culham Science Centre

222 Land north of Wroxton Fields Quarry, Wroxton

225 Cedars Storage, Benson

248 Thrupp Lane, Radley

249A High Cogges Farm, Witney

250 Broughton Poggs Business Park

262 Lower Heath Farm, Cottisford

265 Woodeaton Quarry

277 Land adjacent the B480, Chalgrove

280 Oxford Shooting School, Enstone Airfield

281 Farringdon Quarry, Farringdon/Little Coxwell

286 Wally Corner, Berinsfield

288 Brize Norton Road, Minster Lovell

MINERAL SITES

SHARP SAND AND GRAVEL

Sites Proceeding to Stage 3b: Detailed Technical Assessment

SG-08 Lower Road, Church Hanborough SG-09 & SG- Land north of Drayton St Leonard and 59 Berinsfield and land at Stadhampton SG-11 & SG- Land situated Northeast of Sonning Eye 65 (Caversham phases ‘D’ & ‘E’) SG-17 Land at Culham

SG-18 Land near Standlake

SG-20 Land between Eynsham & Cassington

SG-20a Land between Eynsham & Cassington

SG-20b Land between Eynsham & Cassington

SG-23 Windrush North, Gill Mill

SG-27 Vicarage Pit Cogges Lane

SG-29 Sutton Farm, Sutton

SG-42 Nuneham Courtenay

SG-60 White Cross Farm

SG-62 Appleford

SG-63 Finmere Quarry

SG-67 Sutton Wick Quarry

Sites Eliminated

SG-03 Land adjacent to Benson Marina

SG-04 Land at Mead Farm

SG-05 Land to the East of Cassington Quarry

SG-12 Land South of Chazey Wood

SG-13 Land at Shillingford SG-15 (incl SG-58 & SG- Dairy Farm 58a) SG-16 Land at Stonehouse Farm

SG-36 Land at Friars Farm

SG-37 Land at Grandpont and South Hinksey

SG-41 North of Lower Radley

SG-61 Mains Motors CRUSHED ROCK (CR) SITES

Sites Proceeding to Stage 3b: Detailed Technical Assessment

CR-07 Adjacent to Whitehill Quarry

CR-10 Burford Quarry SW Extension

CR-13 Dewars Farm Quarry East Extension

CR-15 Land off the B4100, Baynards Green

CR-19 Dewars Farm Quarry South Extension

Sites Eliminated

CR-03 Southern Extension to Rollright Quarry

CR-08 Castle Barn Quarry

CR-18 Shipton-on-Cherwell Quarry SOFT SAND (SS) AND CRUSHED ROCK (CR) SITES

Sites Proceeding to Stage 3b: Detailed Technical Assessment SS-03 and Hatford Quarry South Extension CR-17 SS-07 and Home Farm, Shellingford CR-24 SS-08 and Shellingford Quarry (Western Extension) CR-16 SS-12 and Land at Chinham Farm, Chinham Hill CR-12 SS-15 and Hatford Quarry North Extension CR-11 SS-16 and Hatford Quarry Stanford Extension CR-21

SS-18 and Hatford Quarry West Extension CR-22 SS-19 and Home Farm, Carswell Quarry CR-23 SOFT SAND (SS) SITES

Sites Proceeding to Stage 3b: Detailed Technical Assessment

SS-04 Land at Pinewood Road

SS-05 Land at Kingston Bagpuize

Sites Eliminated Land north and south of A420 near Fyfield and SS-17 Tubney

The justification for eliminating sites is provided on the detailed assessment proformas included at Appendix A.

Sites which have proceeded for detailed technical assessment at Stage 3b have been further assessed. The assessment methodology and the outcome of the Stage 3b assessment is explained in Section 3.

Stage 3b: Assessment Methodology

Further detailed technical assessment, comprising Stage 3b of the assessment methodology, has been carried out for those sites considered potentially suitable for allocation following the initial screening exercise.

The detailed assessment has drawn on the experience and local knowledge of specialists at Oxfordshire County Council. This specialist knowledge includes advice from ecologists, landscape architects and highway officers.

Additional data and information has also been requested from the site promoters where necessary in order to ensure that the site assessments have been based on the most up to date and relevant information.

The planning history of each site has been recorded to assist in reaching a judgement on the potential suitability of the site.

An assessment has also been carried out against the relevant site selection criteria in the Core Strategy, e.g. policies M3, M4, W3, W4 and W5.

Given the nature of the specialist information available, a qualitative assessment of the merits or otherwise of each site was undertaken as opposed to assigning each criteria a RAG sensitivity score as envisaged in the original Site Methodology in August 2018. This approach provides a robust basis for the comparative analysis of nominated sites.

The sites proceeding to Stage 3b are as set out in Table 2 above and comprise: • 25 sites nominated for potential waste management uses; • 46 sites nominated for potential mineral extraction; - 15 Sand and Gravel; - 8 Soft Sand and Crushed Rock Sites; - 2 Soft Sand; and - 5 Crushed Rock.

Outcome of Stage 3b: Detailed Site Assessment

The outcome of the initial screening and the detailed technical assessment for each of the sites assessed at Stage 3b is provided at Appendix B.

Each site assessment concludes on whether the site may be a suitable reasonable alternative for allocation in the Sites Plan.

Oxfordshire County Council will use the outcome of this site assessment to identify reasonable alternative mineral and waste sites and the preferred options that are considered to best meet the identified requirement for minerals provision and waste management in the Core Strategy. Those sites that are considered to have potential may be allocated in the Oxfordshire Minerals and Waste Local: Part 2 – Site Allocation (Sites Plan) to be consulted on as part of the consultation on the draft Plan (Regulation 18).

Appendix 1 Stage 3a Eliminated Sites

Site 005 – Playhatch Quarry, Playhatch

Site Information (as nominated in 2017) Site Location Playhatch Quarry, Playhatch

Grid Reference SU 740764

Administrative Area South Oxfordshire

Parish Eye and Dunsden

Site Nominee(s) Grabloader Ltd

Proposed Aggregate and soil recycling Development facility for construction and demolition waste 100,000 tpa Site Area 4.5ha

Existing capacity 70,000 tpa

Annual Throughput 18,303.46 tonnes (2017) 31,121.00 cubic metres (2016) 32,794.00 cubic metres (2015)

Existing land use Existing recycling facility for construction and demolition waste Access Existing access onto Playhatch (within 350m of A4155) Current levels and 40 tipper/grab lorry types of traffic movements movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site currently operates as an aggregate and soil recycling facility with an operational (Policy W4) capacity of 70,000 tpa. The site is therefore considered strategic in accordance with Policy W4. • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. However, the site lies 0.4km from the Oxfordshire Lorry Route Network (A4155) to the south west of the site. • Site does not lie within 200m of SAC • Site does not lie within AONB District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies within 2km of an AONB. Water Environment and Flooding • Site overlies Source Protection Zone 2 and 3. (Policy C3 and Policy C4)) • Site lies within Flood Zone 1. • The EA advise there is a potential groundwater quality issue that might need to be risk assessed prior to the development. The site is located in the outer source protection zone for a public water supply so groundwater is sensitive. Air Quality (Policy C5) • Site lies within 1km of the Reading AQMA. • Existing site operation processes 70,000tpa. Soil Resources (Policy C6) • Site within an area of Grade 2 and 3 agricultural land, although site is already developed. Historic Environment (Policy C9) • Historic buildings located within 500m to the south of the site. Transport and Access (Policy • Site lies within 500m of A4155 access. C10) • Site lies within 3km of an area with a history of serious RTI’s. • No AM peak or PM peak traffic congestion areas identified within close proximity to site. • Site currently operates as an existing waste site. No works required to access. Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • There are a number of residential properties within 250m to the south of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt.

Cumulative Impact (minerals and • Site does not lie within 3km of any waste sites. waste sites) • Site lies within 3km of an existing minerals site: Caversham Quarry. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of two nominated minerals sites: SG-11 and SG-65 Land north east of Sonning Eye (Caversham phases 'D' & ‘E’). Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Conclusion

The site currently operates as a soil and aggregate recycling facility with a reported operational capacity of up to 70,000 tpa.

Recent throughputs of waste material to the site over the last three-years have reportedly been between 18 – 33,000 tpa, with around 40 vehicle movements per day. The site connects via Playhatch – a secondary minor road – to the Oxfordshire Lorry route Network (A4155) to the south-west.

No footways are provided along much of the Playhatch route to the south. Residential properties and a pub lie adjacent to this route where a 30mph speed limit also applies. Ground water is sensitive at this location due to the underlying Source Protection Zone.

The site does not lie within a suitable distance to any urban area and is contrary to Policy W4 in this respect.

Based on this baseline information, the site has limited potential to further intensify its use and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 013: Ewelme No. 2 Site, Goulds Grove, Ewelme

Site Information (as nominated in 2018) Site Location Ewelme No. 2 Site, Goulds Grove, Ewelme Grid Reference SU 646 905 Administrative Area South Oxfordshire Parish Benson and Ewelme Site Nominee(s) Grundon Proposed Permanent retention of waste transfer station for non- Development hazardous waste, recycling facility for inert and non- hazardous waste and recycling facility for non- hazardous road sweepings Site Area 0.2 ha Existing capacity Non-hazardous and inert recycling: Up to 10,000 tpa Non-hazardous (road sweepings) recycling: Up to 15,000 tpa Non – hazardous waste transfer: Up to 50,000 tpa Annual Non-hazardous and inert recycling: Throughput (tpa) 2017:2,438 2016:2,672 2015:2,558 Non-hazardous road sweepings recycling: 2017:6,299 2016:11,217 2015:5,449 Non – hazardous waste transfer: 2017:47,480 2016:48,791 2015:46,915 Existing land use Existing waste transfer station for non-hazardous waste and recycling facilities for inert and non- hazardous wastes (including road sweepings), all permitted to Dec 2031 Access Existing access onto Old London Road (within 2km of A4130)

Current Non-hazardous and inert recycling: 4 (daily) levels and Non-hazardous recycling: 6 (daily) Non – hazardous waste transfer: 25 (daily) types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site operates as a temporary waste management facility. (Policy W4) • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. • Site lies within the Chilterns AONB. • Site does not lie within 200m of a SAC. • Site lies within 2km of access onto the Oxfordshire lorry route network (A4130) to the south. District Local Plan Allocation • The site does not conflict with a district local plan allocation. Biodiversity and Geodiversity • Site does not lie within 5km from International / European designated sites. (Policy C7) • Site does not lie within, or adjacent to ancient woodland. • Site does not lie within 1km from SSSI, NNR and protected species. • Site does not lie within 500m from a Local Wildlife Site, SINC or LNR. • Woodland Trust advise the site encompasses part of Biodiversity Action Plan (Common Land) and is in close proximity to Veteran Tree (Pendunculate Oak BAP SU64989093 OAK- SU64619100). Landscape / Visual (Policy C8) • Site lies within AONB (Chilterns) as confirmed by Natural England. Water Environment and Flooding • Site does not overlie a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site does not lie within close proximity to AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land although site is already developed. Historic Environment (Policy C9) • Conservation area lies approximately 200m to the north. • Listed buildings lie within 300m to the north; however, lorry routing could avoid these. Transport and Access (Policy • Site lies within 2km of access onto A4130 to the south. C10) • No access improvements required. • AM peak time congested area lies in close proximity to the south. • Site lies near to area with history of slight to serious RTIs (notably along Beggarsbush Hill).

Public Rights of Way (Policy C11) • Series of public rights of way intersect site, however site is operational, and routes appear active. Health and Amenity (Policy C5) • Residential dwellings located within 400m to the west. • RAF Benson Community School lies within 700m to the west. Green Belt (Policy C12) • Site does not lie within the Green Belt Cumulative Impact (minerals and • Site lies within 3km of four existing waste sites: Battle Farm, Oakley Wood, Ewelme No 1 and waste sites) Mains Motors. • There are no existing minerals sites within 3km of the site. • Site lies within 3km of five nominated waste sites: 013 Ewelme No. 2 Site, 138 Woodside, Old Henley Rd, 152 Ewelme No. 1 Site, 224 Ambrose Quarry and 225 Cedars Storage. • Site lies within 3km of a nominated minerals site: SG-61 Mains Motors. Aerodrome Safeguarding (Policy • Site lies within two aerodrome safeguarding areas (RAF Chalgrove and RAF Benson). M10)

Conclusion

The site currently holds planning consent to operate as a waste management facility until December 2031 – the end of the plan period. Therefore, at this stage, it is not considered appropriate to consider the site for its potential to provide further waste management capacity outside of the plan-period. However, there may potentially be opportunities to promote this site further when reviewing the current adopted plan. Should this be the case, there is potential for cumulative impacts to arise which would require further assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 030 – Shipton on Cherwell Quarry, Kidlington

Site Information (as nominated in 2018) Site Location Shipton on Cherwell Quarry, Kidlington

Grid Reference SP478173

Administrative Area Cherwell

Parish Shipton-on-Cherwell and Thrupp

Site Nominee(s) Shipton Limited

Proposed Inert Landfill Development Inert (CDE) Waste Recycling including Recycled Aggregates

Site Area 6 ha

Existing capacity Unknown

Annual Throughput Unknown Existing land use Quarry with existing waste facility.

Access Existing access onto A4095

Current levels and Unknown types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is adjacent to the Shipton on Cherwell Quarry and its use as a potential waste site (Policy W4) would be in conjunction with mineral working (CR18). • The site is located within 15km of Oxford. • The site has access to the Oxfordshire Lorry Route Network (A4095). • Site is not located within an AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • The site is adjacent to the Shipton-on-Cherwell & White Hill Farm Quarries SSSI and Bunkers (Policy C7) Hill Quarry Local Wildlife Site. • Priority Habitat Creation and Restoration area within 600m south of site. • Ancient Woodland is approximately 350m east of site. • Site lies in excess of 5km from international/European designated sites. • Site does not lie in close proximity to a National Nature Reserve and Local Nature Reserve. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site lies adjacent to flood zone 2 and 3. (Policy C3 and Policy C4)) • Site is not located within a source protection zone. • Site does not overlie a secondary aquifer. Air Quality (Policy C5) • Site located over 1km from an AQMA. Soil Resources (Policy C6) • The site is within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site adjacent to a conservation target area. • A number of listed buildings are within 400m of the site including the listed Shipton lift bridge and four listed buildings to the south of the site at Shipton-on-Cherwell. • Site lies within 300m of a Scheduled Monument (Deserted village of Hampton Gay). • Site lies within 2.5km of a Grade II listed Park and Garden (Kirtlington Park) to the north east and with approximately 3km to Blenheim Park to the south west. Transport and Access (Policy • Site located within 1.2km of access onto the Oxfordshire Lorry route Network (A4095) C10) assuming the existing access to Shipton-on Cherwell Quarry can be used. • Site lies in close proximity to areas identified with AM and PM peak traffic congestion, particularly the A4260.There are no areas with a history of high or serious RTIs within proximity of the site.

Public Rights of Way (Policy C11) • A public footpath is adjacent to the southern boundary of the site. Health and Amenity (Policy C5) • The Site is within 50m of Shipton-on-Cherwell to the north east of the village. There are numerous residential properties at Shipton-on-Cherwell. Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration is proposed on the site. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site.. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of a nominated minerals site: CR-18 Shipton on Cherwell Quarry. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport aerodrome safeguarding area. M10)

Conclusion

The site is adjacent to the Shipton on Cherwell Quarry and is within the Green Belt. Its use as a waste site would be in conjunction with the prior working of minerals.

The site lies within 15km of Oxford and could therefore suitable to provide strategic, non-strategic and small-scale waste management capacity in accordance with Policy W4.

However, there are numerous residential properties in Shipton-on-Cherwell, adjacent to the site which also lies in close proximity to a number of sensitive environmental designations.

The site is therefore considered to have limited potential for waste development and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 138 – Woodside, Ewelme

Site Information (as nominated in 2008) Site Location Woodside, Old Henley Road, Ewelme Grid Reference SU648893

Administrative Area South Oxfordshire

Parish Benson

Site Nominee(s) Mains Motors LTD

Proposed Energy from waste facility for Development treating residual MSW

Site Area 13 ha

Existing capacity 20,000 tpa

Annual Throughput 759.040 tpa (2006) 945.921 tpa (2007)

Existing land use Existing MRS/ELV site.

Access Existing access onto Old London Road (within 1km of A4130).

Current levels and 60 (daily) types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is not within 15km of Oxford, 5km of a large town or within 2km of the nearest small (Policy W4) town. • The site is 900m from the Oxfordshire Lorry Route network (A4130). • The site located in an AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • The Woodland Trust advises that the site forms the north, west and part of the south boundary (Policy C7) of Ancient Woodland (AW) Mogpits Wood (5.3ha) and is also adjacent to small boundary of AW Oakley Wood (7.6ha). • Site located in excess of 1km from SSSI, NNR and protected species. • SSSI lies 2.5km to the northeast of the site. • Little Wittenham SAC lies approximately 8.2km to the north west of the site. • Site located in excess of 500m from a SINC or LNR. • Ewelme Watercress Beds Local Nature Reserve lies 2km north of the site. • Mongewell Woods Proposed Local Wildlife Site lies 2km south of the site. Landscape / Visual (Policy C8) • Site lies within the Chilterns AONB.

Water Environment and Flooding • Site overlies a principal and secondary aquifer. (Policy C3 and Policy C4)) • Site does not lie within a flood zone or source protection zone.

Air Quality (Policy C5) • Site not located within 1km of an AQMA. • Natural England advises that this site will require further assessment in terms of air pollution effects on Shirburn Hill and Aston Rowant SACs arising from residual waste treatment. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There is a single listed building at Gould’s Grove Farm 350m to the north west. • Scheduled Monument (Site of Manor House and Royal Palace) lies 1.8km north of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Fairmile Hospital Grade II listed Park and Garden lies 5.4km southwest of the site. • Grade II listed building lies 400m northwest of the site. Transport and Access (Policy • Access to the Oxfordshire Lorry Route Network (A4130) from the site is via Old London Road. C10) A4130 is approximately 1km form the site. • There is a cluster of residential properties at the junction with the A4130. • No AM or PM peak traffic congestion identified within proximity to the site.

© Adams Hendry Consulting Ltd. 38 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • The site lies within close proximity to an area with history of RTI’s. Public Rights of Way (Policy C11) • There is a public right of way adjacent to the west boundary and a second public right of way adjacent to the east boundary. Health and Amenity (Policy C5) • There is one residential property approximately 160m to the north west of the site and a second cluster of three houses 225m to the east. • Dwellings at Gould’s Grove Farm lie 400m to the northwest of the site. Green Belt (Policy C12) • The site is not located within the Green Belt. Cumulative Impact (minerals and • Site lies within 3km of four existing waste sites: Battle Farm, Oakley Wood, Ewelme No 1 and waste sites) Ewelme No 2. • There are no existing minerals sites within 3km of the site. • Site lies within 3km of three nominated waste sites: 013 Ewelme No. 2 Site, 152 Ewelme No. 1 Site and 224 Ambrose Quarry. • Site lies within 3km of a nominated minerals site: SG-61 Mains Motors. Aerodrome Safeguarding (Policy • The site lies within the RAF Chalgrove aerodrome safeguarding. M10)

Conclusion

The site currently operates as an MRS/ELV site within the Chilterns AONB. The site nomination is from 2008 and it is not known whether the site remains available.

The site does not lie within the Mineral Strategic Resource Area or within the Mineral Safeguarding Area.

A number of other constraints restrict the potential use of the site for mineral extraction including its proximity to ancient woodland and its location ,overlying principal and secondary aquifers.

Due to these constraints, the site is considered to have limited potential as a mineral working site for sharp sand and gravel and will not be subject to further detailed assessment as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 152 - Ewelme No. 1 Site, Ewelme

Site Information (as nominated in 2018) Site Location Ewelme No. 1 Site, Ewelme

Grid Reference SU 646 902

Administrative Area South Oxfordshire

Parish Benson

Site Nominee(s) Grundon

Proposed Hazardous waste recycling Development and preparation for recovery, up to 5000 tpa Site Area 0.35 ha

Existing capacity Unknown

Annual Throughput Unknown

Existing land use Hazardous waste transfer and recycling; permanent facility Access Existing access (within 350m of Old London Road) Current levels and Unknown types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • This is an existing waste site, but as the existing site capacity is not known its strategic value (Policy W4) as a waste site is unknown. • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. • Site lies within 2.5km of the Oxfordshire Lorry Route (A4130) to the south east. • The site is not within 200m of a SAC. • The site lies within the AONB. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies within AONB (Chilterns). Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • A flood zone 3 area lies within 500m to the north. Air Quality (Policy C5) • Site does not lie within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land; however, site is already developed. Historic Environment (Policy C9) • Conservation area lies approximately 700m to the north. • Listed buildings lie within 800m to the north of the site; however, lorry routing could avoid these. Transport and Access (Policy • The closest access to the Oxfordshire Lorry Route is via the A4130 to the south. This is C10) reached via Clack’s Lane and Old Icknield Way which narrow to a single-track width in places. • Site likely to impact existing congested area (AM peak time) to the south. • Site lies near to area with history of slight to serious RTIs (notably along Beggarsbush Hill). Public Rights of Way (Policy C11) • No footpath within the site. There is a footpath directly adjacent to the site. Health and Amenity (Policy C5) • There are residential properties within 350m of the site boundary and further properties within 450m of the site. • RAF Benson Community Primary School lies approximately 1km to the north west of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Cumulative Impact (minerals and • Site lies within 3km of four existing waste sites: Battle Farm, Oakley Wood, Ewelme No. 2 and waste sites) Woodside. • There are no existing minerals sites within 3km of the site. • Site lies within 3km of four nominated waste sites: 013 Ewelme No. 2 Site, 138 Woodside, Old

© Adams Hendry Consulting Ltd. 42 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Henley Rd, 224 Ambrose Quarry and 225 Cedars Storage. • Site lies within 3km of a nominated minerals site: SG-61 Mains Motors. Aerodrome Safeguarding (Policy • Site lies within two aerodrome safeguarding areas (RAF Chalgrove and RAF Benson). M10)

Conclusion

The site is an existing hazardous waste management. The Site which lies within the AONB and does not lie within a suitable distance to any urban area as identified within Policy W4.

Access onto the Oxfordshire Lorry Route Network (A4130) lies 2.3km to the south east, this route prevents vehicles passing through the Village of Benson and properties to the east of RAF Benson. The route is accessed via Old London Road a single carriageway which does not provide pedestrian walkways and is subject to a national speed limit restriction. A number of residential properties reside at the junction to both of these routes.

Based on the outcome of the initial screening, this existing site appears to have limited potential to further intensify or diversify its current waste management activities.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 180 – Elmwood Farm, Black Bourton

Site Information (as nominated in 2008) Site Location Elmwood Farm, Black Bourton Grid Reference SP282050

Administrative Area West Oxfordshire

Parish Black Bourton

Site Nominee(s) Goodwood Recycling Ltd

Proposed Waste wood recycling facility. Development

Site Area 2 ha

Existing capacity Unknown

Annual Throughput 1400 tpa (2007) 1400 tpa (2006)

Existing land use Processing virgin wood (not waste) Access Existing access onto Burford Road Current levels and 6 vehicle movements per day types of traffic allowed due to planning constraints movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is permitted to process virgin wood, up to 4,000 tpa and is not an existing waste (Policy W4) management facility. • Site lies within 2km from the nearest small town (Carterton). • The site is located off Burford Road, which is 1.5km from the Oxfordshire Lorry Route Network (B4020). • The site is not within 200m of a SAC (only relevant to strategic and non-strategic sites). • The site lies within the AONB (only relevant to strategic and non-strategic sites). District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Alvescot Meadows SSSI is located 350m to the west of the site. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • The site is not located on agricultural land. Historic Environment (Policy C9) • There are numerous listed buildings to the south of the site (closest is approximately 700m to the south of the site) along Burford Road. Transport and Access (Policy • The site is located off Burford Road, which connects the site to the Oxfordshire Lorry Route at C10) the B4020. The route from the site to the B4020 passes numerous residential properties. • The site does not lie within close proximity to an area with a history or RTI’s. • No AM peak traffic congestion is identified within proximity to site, however there may be an impact on PM congestion along the A4095. Public Rights of Way (Policy C11) • Part of the site’s access road is a public right of way (151B/11). Health and Amenity (Policy C5) • The closest residential property is approximately 350m to the east. • A number of residential properties align Burford Road which provide access onto the Oxfordshire Lorry Route Network. Green Belt (Policy C12) • Site is not located in the Green Belt. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site. waste sites) • There are no existing minerals sites within 3km of the site.

© Adams Hendry Consulting Ltd. 46 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 3km of three nominated minerals sites: SG-15 Dairy Farm, SG-58 Chestlion Farm and SG-58a Manor Farm. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Conclusion

The facility operates as a virgin wood processing facility with a permitted throughput of up to 4,000tpa. It is not an existing waste site.

The site lies within 2km to the center of Carterton, although does not lie within 15km of Oxford or 5km to any large town as identified within Policy W4. The site therefore is deemed appropriate to provide small-scale waste management capacity in accordance with this policy.

Access onto the Oxfordshire Lorry route Network (B4020) lies approximately 1.25km to the south. Access to this route is via Burford Road a narrow single carriageway which does not provide pedestrian walkways along much of its route, although is aligned by wide grass verge areas suitable for pedestrian refuge. This route is also aligned by residential properties.

Based on the outcome of this initial screening assessment the site appears to have limited capacity for intensification or diversification and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 217 – Culham No.4 Site, Culham Science Centre

Site Information (as nominated in 2018) Site Location Culham No.4 Site, Culham Science Centre

Grid Reference SU533963

Administrative Area South Oxfordshire

Parish Clifton Hampden

Site Nominee(s) UKAEA

Proposed Residual Waste Treatment Development

Site Area 7.4 ha

Existing capacity Unknown

Annual Throughput Unknown

Existing land use Facility for the processing of radioactive materials and controlled waste

Access Existing access onto Thame Lane (within 1.5km of A415)

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site lies within 5km of Abingdon and 15km from Oxford. (Policy W4) • Site lies approximately 1.25 km from the Oxfordshire Lorry Route (A415). • The site is not located in an AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • Site lies adjacent to the Culham Science Centre policy area RUR3 and 5 in the adopted South Oxfordshire Local Plan. South Oxfordshire District Council (SODC) advise that there is an overlap of this site with a proposed strategic allocation in the emerging Local Plan. SODC also advise the site is also linked to the proposed Housing and Infrastructure Fund and a proposed bypass for Culham and Clifton Hampden supported by the County Council and this needs to considered. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. • The Woodland Trust advise the site borders a Biodiversity Action Plan Priority Habitat (Deciduous Woodland) (SU53349683). Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within Flood Zone 2 or 3 or a source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. • Natural England advise further assessment is required to rule out potential indirect or to inform mitigation in regards air quality effects on the Little Wittenham and Cothill SAC. Soil Resources (Policy C6) • The site is not classified as agricultural land. Historic Environment (Policy C9) • The site is adjacent to the Nuneham Courtney historic parkland (Grade I listed Park and Garden). • Historic England advise site is within the setting of the listed heritage assets and the potential impact should be taken into account in deciding whether the site is suitable for waste management. Transport and Access (Policy • The Oxfordshire Lorry Route is connected to the site via roads associated with the Culham C10) Science Centre. • This AM and PM congestion is identified in the Oxfordshire Local Transport Plan on the A415 in proximity to the site. • There is no RTI history within 3km of the site.

© Adams Hendry Consulting Ltd. 50 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Public Rights of Way (Policy C11) • There is a public right of way which runs adjacent to the southern boundary of the site (Thame Lane). Health and Amenity (Policy C5) • No residential dwellings or public open space within 1km of site. Green Belt (Policy C12) • Site lies within the Green Belt and is not an existing waste site. Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Didcot Strategic STW and Upper Farm. waste sites) • Site lies within 3km of an existing minerals site: Sutton Courtenay Quarry (Bridge Farm). • Site lies within 3km of two nominated waste sites: 010 Sutton Courtenay Landfill and 248 Thrupp Lane Radley. • Site lies within 3km of four nominated minerals sites: PFA-01 Land at Thrupp Lane, Radley, SG-17 Land at Culham, SG-41 North of Lower Radley and SG-42 Nuneham Courtenay. Aerodrome Safeguarding (Policy • The site lies within the RAF Dalton Barracks aerodrome safeguarding area. M10)

Conclusion

This site lies adjacent to the Culham Science Centre and within the Green Belt. Development within the Green Belt would be inappropriate unless it would involve the replacement of a building, providing the new building is in the same use and not material larger than the one it replaces (NPPF 145).

The site lies within 15km of Oxford and 5km of Abingdon and is therefore deemed appropriate to provide strategic, non-strategic and small-scale waste management capacity in accordance with policy W4 due to its proximity to these areas. The site lies approximately 1.25km to the north of access onto the Oxfordshire Lorry Route Network via the Culham Science Centre estate internal roads. The site is within proximity to National Grid Infrastructure.

Due to the sites location within the Green Belt, it is difficult through this high level screening assessment to properly establish its potential to provide waste management capacity. This site will not be considered further as part of this assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed . assessment

Site 222 – Land to the north of Wroxton Fields Quarry, Wroxton

Site Information (as nominated in 2009) Site Location Land north of Wroxton Fields Quarry, Wroxton

Grid Reference SP 402 424

Administrative Area Cherwell

Parish Wroxton

Site Nominee(s) Peter Bennie Limited

Proposed Use of inert waste for Development restoration

Site Area 21.3 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Former quarry

Access Adjacent to A422

Current levels and Unknown types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • The site lies over 5.5km from access onto the Oxfordshire Lorry Route Network (A361). • The site is not within 200m of a SAC. • The site does not lie within the AONB. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • The Environment Agency consultation response at the Issues and Options stage identified that the site is located on a secondary aquifer and private water supplies are located nearby. This is a potential groundwater quality issue that might need to be risk assessed prior to the development. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There are listed buildings at Balscote to the south west of the site and Wroxton to the east (all within 1km of the site). Transport and Access (Policy • No AM peak or PM peak traffic congestion identified within proximity to site. C10) • There is no RTI history within 3km. Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • Site lies within 1km of residential properties at Wroxton. Green Belt (Policy C12) • Site does not lie within the Green Belt. Cumulative Impact (minerals and • Site lies within 3km of an existing waste site: Alkerton. waste sites) • Site lies within 3km of two existing minerals sites: Wroxton Quarry and Alkerton Quarry. • Site lies within 3km of a nominated waste site: 023 Alkerton Landfill. • There are no nominated minerals sites within 3km of the site. Aerodrome Safeguarding (Policy • The site is not located within aerodrome safeguarding area. M10)

The site nomination form dates back to 2008. It is not known if this site is still available. The site is not on the Oxfordshire Lorry Route and lies over 5km from Banbury. The site also lies a considerable distance away from access onto the Oxfordshire Lorry Route Network (A361).

The site also overlies a principal aquifer.

Given the remote rural location and distance from the Oxfordshire Lorry Route network, this site is not considered to be suitable for a new waste site and will therefore not be considered further.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 225 – Cedars Storage, Benson

Site Information (as nominated in 2007) Site Location Cedars Storage, Benson

Grid Reference SU 624 924

Administrative Area South Oxfordshire

Parish Benson

Site Nominee(s) Main Bros

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates

Site Area 7.7ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Greenfield site

Access Existing access onto B4009

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not operate as an existing waste site. (Policy W4) • The site is located within 15km of Oxford. • Site is not in the AONB or within 200m of a SAC • Site appears to be greenfield. • The site lies approximately 1.3km from access onto the Oxfordshire Lorry Route Network (A4074) via the B4009. District Local Plan Allocation • New residential development is proposed in the made Benson Neighbourhood Plan (2018) for three proposed housing allocations which it is proposed will deliver a new relief road for Benson. • Land for the whole route of a Relief Road is safeguarded, to the north of the village that connects the B4009 at or near Braze Lane in the east to the A4074 or B4009 at or near Elm Bridge roundabout in the west. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • The site lies 1.2km from the North Wessex Downs AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 2 BMV agricultural land. Historic Environment (Policy C9) • Conservation area lies within 350m to the south west of the site. • There are a number of listed buildings along Brook Street, Benson, close to the south of the site (within 500m). Transport and Access (Policy • The site appears would have access to the B4009. Access along the B4009 to the A4074 is C10) through the village of Benson. • No AM peak or PM peak traffic congestion identified within proximity to site. Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • Residential properties are adjacent to the southern boundary of the site and in close proximity to the west of the site. The neighbourhood plan allocates land for further residential development to the north of the B4009, opposite the site. Green Belt (Policy C12) • Site is not located in the Green Belt.

© Adams Hendry Consulting Ltd. 58 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Cumulative Impact (minerals and • Site lies within 3km of 1 existing waste site: Oakley Wood. waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of two nominated waste sites: 013 Ewelme No. 2 Site and 152 Ewelme No. 1 Site. • Site lies within 3km of two nominated minerals sites: SG-03 Land adjacent to Benson Marina and SG-13 Land at Shillingford. Aerodrome Safeguarding (Policy • Site falls within the RAF Chalgrove and RAF Benson aerodrome safeguarding area. M10)

Conclusion

The site was nominated in 2007. It is not known whether it remains available for waste management uses. The adoption of the Benson Neighbourhood Plan (2018), which proposes housing allocations opposite the site and safeguards a route for the new relief road, would potentially conflict with waste management uses on the site. The B4009 connection to the A4074 through the village of Benson is unsuitable for additional traffic associated with waste management uses.

The site appears to have limited potential to provide waste management capacity and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 248 – Thrupp Lane, Radley

Site Information (as nominated in 2009) Site Location Thrupp Lane, Radley

Grid Reference SU 522 978

Administrative Area Vale of White Horse

Parish Radley

Site Nominee(s) H Tuckwell & Sons Ltd

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates Site Area 10 ha

Existing capacity Not known

Annual Throughput Not known

Existing land use Aggregate and cement producer Access Existing access onto Thrupp Lane (within 3km of A415) Current levels and Not known types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 5km of the nearest large town (Abingdon) and within 15km of Oxford. (Policy W4) • Site lies approximately 2.6km to the east of the Oxfordshire Lorry Route Network (A4183/Oxford Road). • The site does not lie within an AONB • The site does not lie with 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site is adjacent to a Local Wildlife Site, east of the site. (Policy C7) • Site located in excess of 5km from International / European designated sites. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not overlie a source protection zone. (Policy C3 and Policy C4)) • Site is within a Flood Zone 2. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • The majority of the site is within Grade 2 BMV Agricultural land, with some Grade 3 to the north of the site. Historic Environment (Policy C9) • Wick Hall and attached walls, Grade II* and Wick Hall Barn, Grade II Listed are located within 500m of the site. • Thrupp Farm Cottages, Grade II Listed are located just over 500m to the west of the site. • Site lies within 500m of a Grade I listed Park and Garden (Nuneham Courtenay). • Site is not located within 1km of a conservation area. Transport and Access (Policy • Site lies approximately 2.6km to the east of the Oxfordshire Lorry Route Network C10) (A4183/Oxford Road). Public Rights of Way (Policy C11) • A BOAT runs adjacent to the western site boundary. Health and Amenity (Policy C5) • There are two properties within 200m north of the site. Green Belt (Policy C12) • The site is within the Green Belt, although is an existing site. Cumulative Impact (minerals and • Site lies within 3km of 1 existing waste site: Culham JET. waste sites) • Site is not within 3km of an existing minerals site. • Site lies within 3km of a nominated waste site: 217 Culham No.4 Site. • Site lies within 3km of four nominated minerals sites: PFA-01 Thrupp Lane, Radley, SG-17 Land at Culham, SG-41 North of Lower Radley and SG-42 Nuneham Courtenay. Aerodrome Safeguarding (Policy • Site falls within the Dalton Barracks, RAF Chalgrove and RAF Benson aerodrome M10) safeguarding areas.

The site currently operates as an aggregate’s supplier and concrete batching site.

The site is accessed via Thrupp Lane to the north of the site, this access appears to be shared with nearby operating companies including construction company Terrafirma. Thrupp Lane is a narrow single carriage way which does not provide pedestrian walkways along its route, this route continues 1km to the north of the site until it leads on to Radley Road and Twelve Acre Road which in turn lead onto the Oxfordshire Lorry Route Network (A4183/Oxford Road). Additional vehicle movements along Thrupp Lane would therefore be a key consideration in promoting this site as a waste development.

The site overlies an area designated as Flood Zone 2 and should therefore be a consideration in promoting this site as a waste development.

There is the potential for cumulative impacts to arise given the sites proximity to a large number of existing and nominated sites

Due to the key considerations outlined above surrounding vehicle access and flood risk, this site is considered to have limited potential and therefore will not be subject to further detailed assessment as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 249A – High Cogges Farm, Witney

Site Information (as nominated in 2009) Site Location High Cogges Farm, Witney

Grid Reference SP373090

Administrative Area West Oxfordshire

Parish South Leigh

Site Nominee(s) High Cogges Farm Partnership

Proposed Composting / Biological Development Treatment

Site Area 2ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Green field

Access Existing access onto High Cogges (within 1.8km of A40 access)

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 2km of Witney and within 15km of Oxford. (Policy W4) • The site is located 1.8km from access to the Oxfordshire Lorry Route Network (A40). • Site is not located within AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within an AQMA. • Natural England advise the site may require further assessment in terms of air pollution effects on Ducklington Mead SSSI, depending on the energy input into the anaerobic digester.” Soil Resources (Policy C6) • Site within an area of Grade 3 BMV agricultural land. Historic Environment (Policy C9) • High Cogges Farm House (Grade II Listed) is located approximately 130m to the east of the site. Transport and Access (Policy • Prior to access onto the Oxfordshire Lorry Route Network (A40), access would likely be via C10) High Cogges and South Leigh Road which are both single track roads with no pedestrian walkways and soft verges. • A traffic sign at the access to South Leigh Road states ‘Unsuitable for heavy goods vehicles’. These routes then lead onto the B4022 which is a single carriageway. • Possible AM peak or PM peak traffic congestion identified within proximity of site. • Site lies in close proximity to area with history of RTIs. Public Rights of Way (Policy C11) • Public right of way runs adjacent to the west boundary of the site. Health and Amenity (Policy C5) • Residential properties lie within 200m to the east of the site. • Residential properties lie adjacent to the access route. Green Belt (Policy C12) • Site is not located in the Green Belt. Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Gill Mill Quarry and T&B Motors. waste sites) • Site lies within 3km of an existing minerals site: Gill Mill Quarry.

© Adams Hendry Consulting Ltd. 66 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 3km of two nominated waste sites: 233 Witney STW and 249B High Cogges Farm. • Site lies within 3km of a nominated minerals site: SG-23 Windrush North, Gill Mill. Aerodrome Safeguarding (Policy • Site falls within the RAF Brize Norton and London Oxford Airport aerodrome safeguarding M10) areas.

Conclusion

The site does not operate as an existing waste site. Its current strategic value is therefore unknown at this stage.

The site is a greenfield site and appears to be in use for agricultural purposes. The site lies within 2km of Witney and within 15km of Oxford. The site is therefore suitable in terms of scale and proximity to these areas to provide Strategic, non-strategic and small-scale waste management capacity in accordance with Policy W4.

The site is located 1.8km from access to the Oxfordshire Lorry Route Network (A40). Prior to access onto the Oxfordshire Lorry Route Network (A40), access would likely be via High Cogges and South Leigh Road which are both single track roads with no pedestrian walkways and soft verges. A traffic sign at the access to South Leigh Road states ‘Unsuitable for heavy goods vehicles’. These routes then lead onto the B4022 which is a single carriageway.

Residential properties lie within 200m to the east of the site and residential properties lie adjacent to the access route along High Cogges.

The site is considered to have limited potential to provide waste management capacity and will not be subject to further detailed assessment as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 250 – Broughton Poggs Business Park

Site Information (as nominated in 2009) Site Location Broughton Poggs Business Park, Broughton Poggs Grid Reference SP230042

Administrative Area West Oxfordshire

Parish Filkins and Broughton Poggs

Site Nominee(s) Recycle-lite.com

Proposed Waste collection, Development reprocessing and transfer facility including MRF for recyclable materials Site Area 0.35 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Unknown

Access Access onto A361

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • The site has good access to the Oxfordshire Lorry Route network (A361) • Site is not in the AONB or within 200m of a SAC • Site appears to be in industrial/storage use. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies 1.9km from the Cotswolds AONB. Water Environment and Flooding • Site is within Flood Zone 3. (Policy C3 and Policy C4) • EA noted that the site is located on a secondary aquifer and private water supplies are located nearby. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies in close proximity to the Filkins Conservation Area (within 500m of the site). • There are numerous Listed buildings in Filkins within 1km of the site. Transport and Access (Policy • The site is over 3km from its closest urban area (Carterton). C10) • Possible AM peak traffic congestion identified within proximity to site (Filkins). • There is a single ‘fatal’ RTI history on the A361 within 3km of the site. Public Rights of Way (Policy C11) • A bridleway is routed in close proximity to the south west boundary. No diversions necessary. Health and Amenity (Policy C5) • There are a number of residential properties in Filkins within 500m of the site. Green Belt (Policy C12) • Site is not located in the Green Belt. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site. Aerodrome Safeguarding (Policy • Site is located within the RAF Fairford and RAF Brize Norton aerodrome safeguarding areas. M10)

The site was nominated 2009 and it is therefore uncertain as to whether this site is still available. A key matter for consideration is that potential impact waste management activity at this site may have on surrounding water bodies. The site overlies Flood Zone 3 and vulnerable groundwater, a stream runs alongside the site and its primary access, although this does not appear to be a classified as a main river.

Due to issues relating to water resources this site is deemed have limited potential to provide waste management capacity and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 262 – Lower Heath Farm, Cottisford

Site Information (as nominated in 2011) Site Location Lower Heath Farm, Cottisford

Grid Reference SP583314

Administrative Area Cherwell

Parish Cottisford

Site Nominee(s) Direct Farm Eggs

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates Site Area 14ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Existing use unknown. Former egg production unit. Access Existing access onto unnamed road (approximately 1.8 km to A43)

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Public Rights of Way (Policy C11) • Footpath tracks along the west side of the site, could be diverted if necessary, to the boundary of the site. Health and Amenity (Policy C5) • There are six residential properties close to the site entrance. Green Belt (Policy C12) • Site is not located in the Green Belt. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site. Aerodrome Safeguarding (Policy • Site is not located within aerodrome safeguarding area. M10)

The site was nominated in 2011, there is therefore uncertainty as whether this site is still available. The site appears to be in agricultural use with a number of large barns to the east of the site.

The site lies approximately 2km to the east of access onto the A43 via a single-track road which restricts access to vehicles over 7.5t. The site does not lie within a suitable distance to an urban area as identified within Policy W4.

Based on this baseline information, the site has limited potential for waste use and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 265 – Woodeaton Quarry, Islip

Site Information (as nominated in 2018) Site Location Woodeaton Quarry, Islip

Grid Reference SP532123

Administrative Area South Oxfordshire

Parish Woodeaton

Site Nominee(s) Mckenna Environmental Ltd

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates Site Area Total size of quarry: 6.5 ha Aggregate recycling area: 1 ha Existing capacity Unknown

Annual Throughput 41,000 tpa (2017) Existing land use Existing waste site in Green Belt.

Access Existing access onto unnamed road (within 600m of B4027)

Current levels and 30 HGVs (tippers) types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site lies within 15km of Oxford and can therefore be considered for a strategic, non-strategic or (Policy W4) small-scale facility in accordance with policy W4. • The closest Oxfordshire lorry Route access is the A34, over 4km from the site. This is via the Wheatley and Bletchlingdon Roads, which run through the village of Islip. • The site currently operates as a waste site. • The site is not located in proximity to an AONB. • The site is not located within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Woodeaton Quarry is a designated SSSI and Local Geological Site. (Policy C7) • The site is within 5km from International / European designated sites (Oxford Meadows SAC). • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site overlies an area of Grade 3 Agricultural Land, although the site is currently used as an aggregate recycling facility and therefore the land is unlikely to be best and most versatile. Historic Environment (Policy C9) • Site lies adjacent to the grounds and archaeological remains of Romano-celtic temple No Woodeaton. • There are numerous listed buildings in Woodeaton within 250m of the site. Transport and Access (Policy • The site is located over 4km from the Oxfordshire Lorry Route. C10) • There is no RTI history within 3km of the site. • Possible PM peak traffic congestion identified within proximity to site (A34). Public Rights of Way (Policy C11) • No public rights of way within the site, or within close proximity to the site area. Health and Amenity (Policy C5) • There are residential properties within 250m of the site to the south. Green Belt (Policy C12) • Site is located within the Green Belt. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

© Adams Hendry Consulting Ltd. 78 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Aerodrome Safeguarding (Policy • Site falls within the London Oxford Airport aerodrome safeguarding area. M10)

Conclusion

The site is an existing aggregate recycling site. The site is already a non-strategic site, however given its Greenbelt location and the distance from the Oxfordshire Lorry Route, it is not considered appropriate to further diversify or intensify the use of this site and therefore this site will not be considered further.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 277 – Land adjacent the B480, Chalgrove

Site Information (as nominated in 2015) Site Location Land adjacent the B480, Chalgrove

Grid Reference SU 653 968

Administrative Area South Oxfordshire

Parish Chalgrove

Site Nominee(s) David Einig Contracting Ltd

Proposed Landfill Development

Site Area 0.6 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Greenfield

Access No apparent site access to the B480 Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • There is no clearly defined access to the site. However, access form the site to the Oxfordshire Lorry Route Network (B480) may be achievable via north of the site and through the existing routes associated with Tower Estate. • Site does not lie within an AONB, or within 200m of a SAC. District Local Plan Allocation • The site does not conflict with a district local plan allocation. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site does not lie within, or in close proximity to AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within Grade 3 agricultural land, although does not exceed an area of 20ha. Historic Environment (Policy C9) • Site does not lie within or lie in close proximity to a conservation area. Transport and Access (Policy • The site does not appear to have access to the B480. The B480 runs north of the village of C10) Chalgove in close proximity to residential properties. • Site does not lie within close proximity to area with history of RTI’s. Public Rights of Way (Policy C11) • The site does not impact on any public rights of way. Health and Amenity (Policy C5) • Site lies within 500m of residential properties. Green Belt (Policy C12) • The site does not lie within the Green Belt. Cumulative Impact (minerals and • There are no existing waste sites within 3km of the site. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Aerodrome Safeguarding (Policy • The site lies within the RAF Chalgrove airport safeguarding area. M10)

The site was nominated in 2015, there is therefore uncertainty as to whether this site is still available.

The site is located in a rural setting with no obvious access onto the Oxfordshire Lorry Route Network (B480), although this may be achieved through access to the north of the site via the existing routes associated with the Tower Estate. Access onto the B480 via this route is approximately 2.3km.

The site appears to have limited potential to provide waste management capacity and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 280 – Oxford Shooting School, Enstone Airfield

Site Information (as nominated in 2018) Site Location Oxford Shooting School, Enstone Airfield Grid Reference SP 438 226

Administrative Area West Oxfordshire

Parish Enstone

Site Nominee(s) David Einig Contracting LTD

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates Site Area 14.7 hectares

Existing capacity Unknown

Annual Throughput 108,000 tpa (2017) 50,000 tpa (2016)

Existing land use Existing waste site (recycling facility for inert waste).

Access Existing access (within 1km of B4022)

Current levels and Average 40 loads per day (20 types of traffic in, 20 out) movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • The site lies approximately 2.8km to the north of access onto the Oxfordshire Lorry Route Network via the B4022 to the west of the site. • The site does not lie within the AONB. • The site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies over 3km from Cotswolds AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 3 agricultural land, although site is already in use as a waste site. Historic Environment (Policy C9) • Tracey Farmhouse Barn Range and Waterwheel (Grade II listed) lies within 1km of the site (to the north east). Transport and Access (Policy • AM peak traffic congestion identified within proximity to site (Enstone Road) to the west of the C10) site. No PM peak traffic congestion identified within proximity to site. • There are 4 slight RTI histories within 3km of the site – two to the north east and 2 to the south west of the site. Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • There are no residential receptors within proximity to the site. Green Belt (Policy C12) • The site does not lie within the Green Belt. Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Downs Road (old FloGas site) and Plot J, waste sites) Lakeside Business Park. • Site lies within 3km of an existing minerals site: Great Tew Quarry. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Conclusion

The existing waste site currently processes over 100,000 tpa. The site does not lie within a suitable distance to an urban area as identified within Policy W4, and over 2.5km to the Oxfordshire Lorry Route Network (A44).

Due largely to the implications surrounding proximity to urban areas and access onto the Oxfordshire Lorry Route Network, the site has limited potential to further intensify or diversify its use.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 281 – Faringdon Quarry, Faringdon

Site Information (as nominated in 2018) Site Location Faringdon Quarry, Faringdon

Grid Reference SU 288 940

Administrative Area Vale of White Horse

Parish Little Coxwell and Great Faringdon Site Nominee(s) Grundon

Proposed Recycling of inert C&D waste Development

Site Area 15 ha

Existing capacity Up to 8,000 tpa

Annual Throughput 4,208 (2017) 4,835 (2016) 5,574 (2015) Existing land use Existing recycling site for inert waste Access Existing access onto A420

Estimated Traffic 2 (daily) Movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 2km of the nearest small town (Faringdon) and does not lie within 15km of (Policy W4) Oxford or 5km of any large-town. • Site is adjacent to the south of the Oxfordshrie Lorry route Network (A420). • The site does not lie within an AONB. • The site does not lie within 200m of a SAC. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site adjacent to Wicklesham and Coxwell Pits SSSI. Very small part of site lies within SSSI. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • The site does not lie within, or close to AONB. • The appears to be well screen from properties to the south of the site through vegetation. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 2 and Grade 3 BMV agricultural land. Historic Environment (Policy C9) • There is a Grade II listed building approximately 330m north of the site. • There are 10 listed buildings in Little Coxwell approximately 400m south west of the site. • There is also a Grade II listed building approximately 660m east of the site. Transport and Access (Policy • Site is adjacent to the south of the Oxfordshrie Lorry route Network (A420). C10) • Site lies within area with a history of RTIs. • Known congested areas lie in close proximity to the site (both AM and PM) on the A420. Public Rights of Way (Policy C11) • Public bridleway runs along the southern edge of the site. Health and Amenity (Policy C5) • Properties on the outskirts of Faringdon are within 150m north of the site. • Properties lie adjacent to the south. • There appears to be residential properties within 700m to the east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Cumulative Impact (minerals and • No existing waste sites lie within 3km of the site. waste sites) • Site lies within 3km of 2 existing minerals sites: Chinham Farm Quarry and Shellingford Quarry. • Site lies within 3km of a nominated waste site: 230 Chinham Farm.

© Adams Hendry Consulting Ltd. 90 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 3km of two nominated minerals sites: SS-07 Home Farm and SS-12 Land at Chinham Farm (Chinham Hill). Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Conclusion

The site benefits from direct access onto the Oxfordshire Lorry Route Network (A420) although does not lie within close proximity to Oxford or any large towns and is therefore not considered suitable for non-strategic or strategic waste management activities.

Commercial and residential premises appear to exist adjacent to the south of the site, although the site appears to be screened through vegetation along this boundary.

Due to the site’s proximity to sensitive receptors to the south the site and proximity to large town and Oxford market areas, there is limited potential for the site to further intensify of diversify its current activity. The site will therefore not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 286 – Wally Corner, Berinsfield

Site Information (as nominated in 2018) Site Location Wally Corner, Berinsfield

Grid Reference SU580956

Administrative Area South Oxfordshire

Parish Berinsfield

Site Nominee(s) FCC Environment Proposed Non-Hazardous (C&I and Development MSW) Waste Recycling Inert (CDE) Waste Recycling including Recycled Aggregates Site Area 0.87 ha Existing Capacity N/A

Annual Throughput N/A

Existing land use Formerly occupied by a civic amenity facility. Land surrounding site was a landfill site now restored as a solar farm. Proposal site is clear of structures. Access Existing access onto Burcot Lane (within 1km of A4074) Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site lies within 15km of Oxford, a strategic, non-strategic or small-scale facility may therefore (Policy W4) be considered in accordance with Policy W4. • Site lies within 800m of the Oxfordshire Lorry Route Network (A4074) Oxford Road, via Burcot Lane. • Site does not lie within 200m of a SAC. • Site does not lie within AONB. District Local Plan Allocation • The Final Publication of the South Oxfordshire Local Plan 2011 – 2034 shows this site to lie within 200m to the ‘Land at Berinsfield’ Proposed Strategic Allocation (Strat 10), a strategic allocation for approximately 1,700 additional homes. Biodiversity and Geodiversity • Site lies within 2.5km of Little Wittenham SSSI. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies within 1.5km of North Wessex Downs AONB. Water Environment and Flooding • Flood zone 3 crosses southern edge of the site. (Policy C3 and Policy C4)) • Site not within a source protection zone. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within grade 2 agricultural land, although site has previously been developed. Historic Environment (Policy C9) • Site does not overlie or lie in close proximity to conservation area. • Site lies within 800m from listed buildings at Queensford Farm south east of the site. • Also listed buildings within 1km of the site in Dorchester and Drayton St Leonard. Transport and Access (Policy • 2 Serious RTIs within 3km north of site on Oxford Road (M&W lorry route). C10) • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies within 800m of the Oxfordshire Lorry Route Network (A4074) Oxford Road, via Burcot Lane. Public Rights of Way (Policy C11) • No public rights of way crossing or adjacent to the site. Health and Amenity (Policy C5) • Dwelling within 300m north of site. • Dwellings at Berinsfield within 500m of site. • Dwellings within 800m south of site at Queenford Farm. • Dwellings on outskirts of Dorchester within 700m of site. Green Belt (Policy C12) • Site lies within the Green Belt.

© Adams Hendry Consulting Ltd. 94 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Cumulative Impact (minerals and • Site lies within 3km of 1 existing waste site: Berinsfield Car Breakers. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of three nominated minerals sites: SG-09 and SG-59 Land north of Drayton St Leonard and Berinsfield and land at Stadhampton and SG-13 Land at Shillingford. Aerodrome Safeguarding (Policy • Site lies within buffer of airport safeguarding (Dalton Barracks) area. M10) • Proposal is for an enclosed operation.

Conclusion

A relatively small site with a history of waste management activities. The site is accessed via Burcot Lane which provides further access onto the Oxfordshire Lorry Route Network (A40) to the west of the site. Burcot Lane – a single carriageway – is subject to a national speed limit restriction, pedestrian walkways along this route are not provided. Heading west, and continuing the approach to the Oxfordshire Lorry Route Network, Burcot Lane leads onto Wimblestraw Road to the south of Berinsfield. This road lies adjacent to residential properties to the north and would be close to a potential strategic housing allocation in Berinsfield.

An area designated as Flood Zone 3 overlies the southern part of the site, and a large body of surface water lies in close proximity to the south west of the site used to facilitate recreational activities. The site also lies within the Green Belt therefore development within the Green Belt would be inappropriate unless it would involve the replacement of a building, providing the new building is in the same use and not material larger than the one it replaces (NPPF 145).

Due to the matters outlined above, the site is considered at this stage to have limited potential to provide waste management capacity and will not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 288 – Brize Norton Road, Minster Lovell

Site Information (as nominated in 2018) Site Location Brize Norton Road, Minster Lovell

Grid Reference SP 313 098 Administrative Area West Oxfordshire

Parish Minster Lovell Site Nominee(s) B&E Transport (Witney) Ltd Proposed Material processing, waste Development segregation, transfer, empty skip storage and parking of vehicles for non-hazardous and construction, demolition and excavation waste Site Area 0.68 ha

Existing capacity 20,000 tpa

Annual Throughout 2017: 17,500 tpa 2016: 12,000 tpa 2015: 12,000 tpa Existing land use Skip waste recycling facility for non-hazardous and construction, demolition and excavation waste. Access Existing access onto B4477

Current levels and 50 HGVs (Daily) types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 5km of Witney. (Policy W4) • Site lies within 600m of access onto the Oxfordshire Lorry Route Network (A40). • The site does not lie within 200m of a SAC. • The site does not lie within an AONB. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site lies within 500m of a SSSI. (Policy C7) • Site lies within 1.3km of Ancient Woodland. • Site located in excess of 500m from a SINC or LNR. • Site located in excess of 1km from NNR and protected species. • Site located in excess of 5km from International / European designated sites. Landscape / Visual (Policy C8) • Site located within 1.4km of an AONB. Water Environment and Flooding • Site does not lie within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 3 agricultural land, although the site is developed. Historic Environment (Policy C9) • A listed building lies within 100m of the site. • Three further listed buildings lie within 250m of the site. • Site lies within 2km of two scheduled monuments. • Site lies within 1.2km of Little Minster Conservation Area. Transport and Access (Policy • Site lies within 600m of the A40. C10) • AM peak traffic congestion identified within proximity to site. • Site lies in close proximity to area with history of RTIs. • Site is an existing skip waste recycling facility - no works required to improve access. Public Rights of Way (Policy C11) • Site does not overlie or lie adjacent to PROW. Health and Amenity (Policy C5) • Site located adjacent to residential dwellings. • Site lies within a residential area with access to amenities to the northern end of the road at its junction with Burford Road. Green Belt (Policy C12) • Site does not lie within Green Belt. Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Claridges Car Breakers and Manor Farm. waste sites) • Site lies within 3km of an existing minerals site: Burford Quarry. • There are no nominated waste sites within 3km of the site.

© Adams Hendry Consulting Ltd. 98 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • There are no nominated minerals sites within 3km of the site. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Conclusion

The site currently operates as a non-strategic waste management facility with a throughput of less than 20,000 tpa.

The site lies adjacent to Brize Norton Road which provides access to the Oxford Lorry Route Network (A40) approximately 600m to the south. Brize Norton Road is subject to a 30mph speed limit restriction with a ‘give-way to oncoming traffic’ traffic calming measure at the south entrance to the road from the A40. There are also signs which advise against heavy goods vehicle movements along this road. Pedestrian walkways are provided along much of this road.

Due to the considerations outlined above, and largely due to the sites proximity to surrounding residential properties, there is limited potential for the site to provide a greater level of diversification from, or intensification of its existing waste management processes. The site will therefore not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site CR-03: Southern Extension to Rollright Quarry

Site Information (as nominated in 2018) Site Location Southern Extension to Rollright Quarry Grid Reference SP282304 Administrative Area West Oxfordshire Parish Rollright Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Development Crushed rock extraction. Extension to Rollright Quarry. Site Area 5.5 ha Estimated annual 80,000 – 100,000 tpa output Estimated Reserves Estimated total yield of c. 600,000 tonnes. (including depth/ Working depth 6.9 -8.5m below ground level. overburden) Estimated overburden of 1.65m including soils. Proposed Restoration Low level agricultural use with elements of geoconservation with retention of exposures of the Chipping Norton Limestone Formation and habitat creation linked to the existing Oakham Quarry LNS. The low-lying agricultural land could support woodland/ plantation afteruse. Access Access onto C70 road (within 2.25km of A3400) Estimated Max daily loads at likely outputs of 20 Traffic loads (40 movements) with additional movements for small loads of walling Movements stone. Year of No later than early 2021. Commencement Lifetime of Planning permission for phase 1 to 2042 Operation and phase 2 to end 2020.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies outside the Mineral Strategic Resource Area and Mineral Safeguarding Area. Strategy – Strategic Resource • Site located in northern part of the County (West Oxfordshire). Areas (Policy M3) • Site is proposed as a potential extension to Rollright Quarry. • Estimated total yield is 600,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. (Policy C7) • There is an area of ancient woodland approximately 1.3km to the north west. • Cross Hands Quarry SSSI lies approximately 1.5km to the south west. • A Local Geological Site, Rollright Flick Quarry, adjoins the site to the north west. Landscape / Visual (Policy C8) • Site lies within the Cotswolds AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4) • Site does not lie within flood zones 2 or 3. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within Grade 3 agricultural land. Historic Environment (Policy C9) • There are listed buildings within 1km of the site to the west at Oakham and to the east at Little Rollright. • Site does not lie within or adjacent to a conservation area. • The Rollright Stones SAM and ‘Iron Age enclosed settlement, and part of trackway 150m north east of the King Stone’ SAM, lie between 1km and 1.2km to the east Transport and Access (Policy • Site lies approximately 2.3km from the A44 access to the south west and approximately 2.5km C10) to the A3400 to the east, both of which are on the Oxfordshire lorry route network. • The site does not lie in close proximity to an area with a history of RTI’s • AM and PM congestion identified along the A44 near Chipping Norton. Public Rights of Way (Policy C11) • A footpath runs adjacent to the southern boundary of the site. Health and Amenity (Policy C5) • The nearest residential properties (Windmill Cottages) are 280m to the south of the site, along the connecting vehicular route to the A44 and A3400. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Potential Cumulative Impact • There are no existing waste sites within 3km of the site. (minerals and waste sites) • Site lies within 3km of two existing minerals sites: Rollright Quarry (Phase I) and Rollright Quarry (Phase II). • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site does not lie within the Mineral Strategic Resource Area for crushed rock extraction, nor does the site lie within the Mineral Safeguarding Area for crushed rock. The site is however proposed as an extension to Rollright quarry.

A key consideration for further mineral development at this site is its setting within the Cotswolds AONB.

Due to the site’s juxtaposition to an existing quarry, a means of vehicle access is currently available to the site and onto a single carriageway which enables access onto the Oxfordshire lorry route network within 2.5km.

Based on the outcome of the initial screening assessment, the site is not considered to have potential for mineral development and will not be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site CR-08: Castle Barn Quarry

Site Information (as nominated in 2009) Site Location Castle Barn Quarry

Grid Reference SP302224

Administrative Area West Oxfordshire

Parish Sarsden and Lyneham Site Nominee(s) PGW&A LLP for The Downs Stone Company Proposed Development Crushed rock extraction. Extension to Castle Barn Quarry. Site Area 9 ha Estimated annual 3,000 - 4,500 tpa output Estimated Reserves Estimated 50,000 cu.m. (approx. (including depth/ 105,000 ts based on conversion estimate for oolitic limestone) overburden) Estimated 15-18m working depth Estimated 3m overburden Proposed Restoration Backfilling and re-grading for agricultural use as currently with phased workings. Access Existing access onto a private estate road (within 500m of A361) Estimated Up to 5 tractor loads of limestone Traffic block per day. Movements Year of Unknown Commencement Lifetime of 4-5 years Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within Mineral Strategic Resource Area. Strategy – Strategic Resource • Site is located in the northern part of the county (West Oxfordshire). Areas (Policy M3) • Site is proposed as a possible extension to Castle Barn Quarry. • Estimated Site yield is 105,000 tons. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies approximately 1.3km of Newclose Copse to the south and Sarsgrove Wood to the (Policy C7) north and approximately 1.4km from the Norrells to the southwest (ancient & semi-natural woodland). • Sargrove Wood SSSI lies approximately 1.2km to the north of the site. • Site lies approximately 5km of Wychwood National Nature Reserve and Cornbury Park Proposed Local Wildlife Site. It is not within 5km of Local Nature Reserve. • Site lies in excess of 5km from International/European designated sites. Landscape / Visual (Policy C8) • Site lies within the Cotswolds AONB Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a Principal Aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • A scheduled monument (Skew Plantation Bowl Barrow) is adjacent to the site to the north and the Roundabout Hillfort SAM lies approximately 1km to the south. • Bowl Barrow scheduled monument lies within 500m of the site to the south east. • A number of listed buildings are located in Sarsden, approximately 1.2 km to the north west of the site. • Sarsden House Registered Historic Park and Garden lies approximately 450 m to the north west of the site. Transport and Access (Policy • The site is located adjacent to the A361, which is on the Oxfordshire lorry route network. C10) • Site lies within close proximity of an area with a history of RTI’s. • No AM peak or PM peak traffic congestion identified within close proximity to site. Public Rights of Way (Policy C11) • A public right of way runs between the two parts of the site.

© Adams Hendry Consulting Ltd. 106 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • The closest residential dwelling is approximately 200m from the site and others lie close to the site (approximately 300m and 700m). • The A361 runs through several villages including Burford, Fulwood and Shipton under Wychwood to the south west and Chipping North to the north east. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site does not impact an aerodrome safeguarding area. M10)

Potential Cumulative Impact • There are no existing waste sites within 3km of the site. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Castle Barn Quarry. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site was nominated in 2009, there is therefore uncertainty as to the current availability of the site. The nominated site does not lie within the Mineral Strategic Resource Area, however, it is proposed as an extension to Castle Barn Quarry.

The site lies within the Cotswold’s AONB and in close proximity to a number of heritage assets including scheduled ancient monuments which lie adjacent to, and in close proximity to the site.

The site also overlies a Principal Aquifer. The A361 passes through a number of towns and villages and the site itself is within 200m of a residential property to the south west of the site.

Based on the constraints identified above as part of this initial screening assessment, the nominated site appears to have limited potential for mineral extraction and should therefore not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site CR-18: Shipton-on-Cherwell Quarry

Site Information (as nominated in 2018) Site Location Shipton-on-Cherwell Quarry

Grid Reference SP482169

Administrative Area Cherwell

Parish Shipton-on-Cherwell and Thrupp

Site Nominee(s) Shipton Ltd

Proposed Development Crushed rock extraction. Extension to Shipton on Cherwell Quarry. Site Area 6 ha Estimated annual 120,000 tpa output Estimated Reserves Estimated yield of 400,000 tonnes (including depth/ Estimated working depth of 15m Estimated overburden of 1.2m overburden) Proposed Restoration Will be returned to agricultural land.

Access Existing access onto A4095. New access arrangement from the A4260 will be implemented in the future. Estimated Unknown Traffic Movements Year of 2018-2019 Commencement Lifetime of Less than 1 year of reserves Operation remaining at existing site.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site outside of the Mineral Strategic Resource Area and outside of the Mineral Safeguarding Strategy – Strategic Resource Area. Areas (Policy M3) • The site lies within the northern part of the County (Cherwell). • Site is proposed as a potential extension to Shipton-on-Cherwell Quarry. • Estimated Site yield is 400,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • The site is adjacent to the Shipton-on-Cherwell & White Hill Farm Quarries SSSI and Bunkers (Policy C7) Hill Quarry Local Wildlife Site. • Priority Habitat Creation and Restoration area within 600m south of site. • Ancient Woodland is approximately 350m east of site. • Site lies in excess of 5km from international/European designated sites. • Site does not lie in close proximity to a National Nature Reserve, Local Nature Reserve or Local Wildlife Site. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site lies adjacent to flood zone 2 and 3. (Policy C3 and Policy C4) • Site is not located within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site located over 1km from an AQMA. Soil Resources (Policy C6) • The site is within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site adjacent to a conservation target area. • A number of listed buildings are within 400m of the site including a Grade II listed bridge on the River Cherwell and the listed Shipton lift bridge and four listed buildings to the south of the site at Shipton-on-Cherwell. • Site lies within 300m of a Scheduled Monument (Deserted village of Hampton Gay). • Site lies within 2.5km of a Grade II listed Park and Garden (Kirtlington Park) to the north east and with approximately 3km to Blenheim Palace to the south west.. Transport and Access (Policy • Site located within 1km of access onto the Oxfordshire Lorry route Network (A4095) assuming C10) the existing assess to Shipton-on-Cherwell Quarry can be used. • Site lies in close proximity to areas identified with AM and PM peak traffic congestion, particularly the A4260. Public Rights of Way (Policy C11) • A public footpath is adjacent to the southern boundary of the site. • Restoration to original ground levels proposed.

© Adams Hendry Consulting Ltd. 110 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • The Site is within 50m of Shipton-on-Cherwell to the north east of the village. There are numerous residential properties at Shipton-on-Cherwell. Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration to original ground levels proposed. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport aerodrome safeguarding area and is located just M10) over 1km to the northeast of the aerodromes take-off and approach surface.

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Shipton Quarry and NW corner of Kidlington TW Depot. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Shipton-on-Cherwell Quarry. • Site lies within 3km of 1 nominated waste site: 030 Shipton Cherwell Quarry. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site is a potential extension to Shipton-on-Cherwell Quarry Site and lies outside of the Mineral Strategic Resource Area and the Mineral Safeguarding Area.

The site lies within the Green Belt and is within 50m of residential properties in Shipton-on-Cherwell. The site also lies in close proximity to London Oxford Airport, and in particular to its take-off and approach surfaces with potential to impact aviation safety.

Due to the constraints outlined and summarised above, there is considered to be limited potential for mineral extraction at this site. The site will not therefore be considered further as part of this assessment process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-03: Land adjacent to Benson Marina

Site Information (as nominated in 2018) Site Location Land adjacent to Benson Marina Grid Reference SU 610 919 Administrative Area South Oxfordshire Parish Benson Site Nominee(s) Folbro Y Limited Proposed Development Sharp sand and gravel extraction. New quarry. Site Area 2 ha Estimated annual Unknown output Estimated Reserves Estimated total yield is 60,000 – (including depth/ 80,000 tonnes Extent of working depth and overburden) overburden unknown Proposed Restoration Extension to the existing River Thames marina facilities at Benson after mineral extraction has been completed. Any restoration would involve extensive landscaping, enhancing the existing hedgerows and wildlife corridors. Access Direct from existing A4074/B4099 roundabout junction. Estimated Unknown Traffic Movements Year of The site is available. As soon as the Commencement site is identified as a preferred location and planning permission is obtained. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within the Mineral Strategic Resource Area or the Mineral Safeguarding Area. Strategy – Strategic Resource • Site located in the southern part of the county (South Oxfordshire). Areas (Policy M3) • Estimated yield is 60-80,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Priority Habitat Creation and Restoration point (Phase 2 North Farm River of Life Project (Policy C7) 2013/14) approximately 2.8km north west of the site. • Marsh Wood (Ancient Woodland) lies approximately 1.8km south east of the site and Ladybrook Copse (Ancient Woodland) lies approximately 2km north of the site. Another area of Ancient Woodland also lies 2.4km west of the site. • Ewelme Watercress Beds (Local Nature Reserve lies) approximately 2.5km to the east of the site. • Little Wittenham SAC (International / European designated site) is approximately 3.5km west of the site. • Site located in excess of 1km from SSSI, NNR and protected species. Nearest SSSI is 3.4km west of the site. • Site located in excess of 500m from a SINC. Landscape / Visual (Policy C8) • Site is adjacent to the North Wessex Downs AONB (separated only by the Thames). • Natural England advise that consideration will need to be given to inter -visibility between the site and AONB. Where this occurs Landscape and Visual Impact Assessment will need to be undertaken to inform consideration of the site for inclusion in the plan. Water Environment and Flooding • Site lies within Flood Zones 2 and 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection Zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 2 agricultural land and a small area of Grade 4 agricultural land. Historic Environment (Policy C9) • Conservation area lies within 200m to the east. • Grade II listed buildings in Benson lie within 350m east of the site. • Grade II listed milestone lies within 700m to the north west on Henley Road. • Historic England advise that the Historic Environment Record is consulted for non-designated archaeological remains as well as the County Archaeologist. Transport and Access (Policy • Site lies adjacent to A4074 Oxfordshire Lorry Route. C10)

© Adams Hendry Consulting Ltd. 114 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site located within an area with history of RTIs (one serious RTI adjacent to the site on the A4074). • No AM peak traffic congestion identified within proximity to site. • PM peak traffic congestion identified on A4074. Public Rights of Way (Policy C11) • Thames Path crosses through the south of the site along the site boundary. Health and Amenity (Policy C5) • Site lies adjacent to residential properties to the south east (caravan park) as well as properties in the wider Benson village area within 100m of the site. • Potential for site to be restored for marina use following extraction. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Chalgrove aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of three existing waste sites: Oakley Wood, Benson STW and Battle Farm. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of one nominated waste site: 225 Cedars Storage. • Site lies within 3km of two nominated minerals sites: SG-09 & SG-59 Land north of Drayton St Leonard and Land at Stadhampton; and SG-13 Land at Shillingford.

Conclusion

This would be a new quarry outside the MSRA and MSA. There are a number of constraints to potential mineral working including the site’s location adjacent to the AONB. The site is also adjacent to a number of residential properties and within 300m of the wider Benson village and 200m of a Conservation Area. The Thames Path runs along its southern boundary.

The site is therefore considered to be unsuitable at this stage and will not be considered further as part of the detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-04: Land at Mead Farm

Site Information (as nominated in 2018) Site Location Land at Mead Farm Grid Reference SP480 113 Administrative Area Cherwell Parish Yarnton Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. Extension to Cassington Quarry. Site Area 7 ha Estimated annual output Unknown Estimated Reserves Estimated total yield is 0.2 mts (including depth/ Estimated working depth of 3.27m Estimated overburden of 0.97m overburden) Proposed Restoration Mosaic of wetland habitats with potential for conservation/amenity purposes. All Hanson operations use progressive restoration techniques. Access Site would be worked with adjacent Stonehouse Farm, Yarnton & share same access arrangements Estimated Traffic Estimated 50 trips by 20t lorry per day which, Movements using typical working day of 7 hours, results in an extra 14 vehicular trips per hour on the highway network. Alternatively, it may be possible to conveyor material to the Cassington Quarry for processing – subject to feasibility. There is now an opportunity to use jet pumping to transport mineral to Cassington for processing – using an existing tunnel under the railway. Year of Not before 2022 Commencement Lifetime of Operation Unknown

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies outside of Mineral Strategic Resource Area although within the Mineral Safeguarding Strategy (Policy M3 and C10 Area (M8) of the OMWLP but is a potential extension to Cassington Quarry. transport) • Site located in the northern part of the county (Cherwell). • Estimated yield is 200,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies 500m to the north of the Oxford Meadows SAC and Pixey and Yarnton Meads SSSI. (Policy C7) Cassington meadows SSSI lies 1.7km south west of the site. • Site does not lie in close proximity to any SPAs or Ramsar sites. • Begbroke Wood (Ancient Woodland) lies 2km north west of the site. • Site does not lie close to any LNRs or NNRs. • Priority Habitat Creation and Restoration Point (Kings Weir Fish Pass Project) lies approximately 800m south of the site. • Dukes Meadow (Proposed Local Wildlife Site) lies 1.2km south east of the site. • Woodeaton Quarry (Local Geological Site) lies 5km east of the site. • Natural England advise the site has the potential to affect the Oxford Meadows SAC and Rushy Meadow, Hook Meadow and the Trap Grounds, and Wytham Ditches and Flushes SSSI sites. Potential impacts include changes to the hydrological regime or water quality and air pollution from traffic and dust deposition. Landscape / Visual (Policy C8) • Site does not lie within an AONB. Water Environment and Flooding • Site does not lie within a Source Protection Zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. • Site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site lies within 1km of an AQMA. • Natural England advise that consideration would need to be given to any impacts from traffic related air pollution or dust deposition. Soil Resources (Policy C6) • Site lies within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • Site lies within 100m of a Grade II listed building to the north of the site (Mead Farmhouse). • Cluster of listed buildings 275m north west of the site (includes Yarnton Manor and Church of St Bartholomew). • Historic England advise, the potential impact on listed buildings will need to be considered. • Grade II listed Park and Garden (Yarnton Manor) lies 200m north west of the site. • Site located within 700m of the Oxford Canal Conservation Area. • Site lies 1.7km to the north of a Scheduled Monument (ring ditches, barrows).

© Adams Hendry Consulting Ltd. 118 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 5km of a World Heritage Site and Grade I listed Park and Garden (Blenheim Palace) to the north west of the site. Transport and Access (Policy • Site lies within 1.4km of the Oxfordshire Lorry Route Network (A44). Access onto the C10) Oxfordshire Lorry Route Network (A44) would likely be via Church Lane, a single-track road with no pedestrian walkways and soft verges. • There may be an opportunity to transport land-won material from this site to the existing processing plant to the south of the adjacent railway line either through an existing tunnel, or via a conveyor system over the existing railway line. The access to the Oxfordshire Lorry route Network would then be via the established access onto the A40 to the south west. • AM and PM peak traffic congestion areas identified in close proximity to site. • Site does not lie in proximity to an area with history of RTIs. Public Rights of Way (Policy C11) • Public footpath on eastern boundary of site (Shakespeare’s Way). Health and Amenity (Policy C5) • The nearest residential dwellings are within 40m to the north-west of site. • Residential properties lie adjacent to the likely access route. Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within London Oxford Airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of two existing waste sites: Worton Farm and Charlett Tyre Yard. (minerals and waste sites) • Site lies within 3km of one existing minerals site: Cassington Quarry. • Site lies within 3km of two nominated waste sites: 009 Worton Farm (Areas C & D) and 261 The Marshes. • Site lies within 3km of three nominated minerals sites: SG-05 Land to the East of Cassington Quarry, SG-16 Land at Stonehouse Farm and SG-20a Land between Eynsham and Cassington.

Conclusion

This site is put forward as a potential extension to Cassington Quarry and appears to be in use for agricultural purposes. The site is within the Green Belt and is outside the mineral strategic resource area.

The site lies within close proximity to the Oxford Meadows SAC. Further detailed assessments would need to be undertaken to determine whether extraction could take place here whilst avoiding significant impacts on the SSSIs in proximity to the site.

Other key potential constraint include proximity to Grade II listed buildings as well as surrounding residential properties to the north.

The site is considered to have limited potential as a mineral working site for sharp sand and gravel and will not be subject to further detailed assessment.

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-05: Land to the East of Cassington Quarry

Site Information (as nominated in 2009) Site Location Land to the East of Cassington Quarry Grid Reference SP 485 108 Administrative Area Cherwell Parish Gosford and Water Eaton Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. Extension to the former Cassington Quarry. Site Area 8.5 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield of 0.23 mts (including depth/ Estimated working depth of 5.98m Estimated Overburden of 1.33m overburden) Proposed Restoration Series of small waterbodies formed using overburden on site and achieved progressively. Opportunity also to create scrapes. Restoration would be designed to link with existing quarry extension. Creation of a lakeside walk. Access Existing purpose-built grade separated access to Cassington Quarry off the A40. Estimated As existing. Max 450,000 t/a Traffic (Cassington plant output capacity) Movements Year of Unknown Commencement Lifetime of Timing subject to other extensions. Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • The site does not lie within the Mineral Strategic Resource Area but does lie within the Mineral Strategy (Policy M3 and C10 Safeguarding Area within the northern part of the County (Cherwell). transport) • The site is proposed as a potential extension site to the former Cassington Quarry. • Estimated yield for the Site is 230,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies less than 50m to the north of the Oxford Meadows SAC and Pixey and Yarnton Meads (Policy C7) SSSI, on the opposite side of the A40. • Site lies within 900m of another area of the Oxford Meadows SAC and Port Meadow with Wolvercote Common & Green SSSI to the south and 2km of a SAC and SSSI to the west. • An area of Ancient Woodland lies 1.3km south of the site and Godstow Halt (Ancient Woodland) lies within 1.8km south of the site. • Begbroke Wood (Ancient Woodland) lies 2.4km north west of the site and Wytham Great Wood lies 2.3km south west of the site. • Priority Habitat Creation and Restoration Point (Kings Weir Fish Pass Project) lies approximately 530m south west of the site. • Dukes Meadow (Proposed Local Wildlife Site) lies 400m south of the site. • Woodeaton Quarry (Local Geological Site) lies within 5km north east of the site. • Site does not lie close to any LNRs, or NNRs. • Natural England have advised that extraction in this area has the potential to affect the Oxford Meadows SAC through changes to hydrological regime or water quality at this water dependant site (and it’s underpinning SSSIs). Consideration would also need to be given to any impacts from traffic related air pollution or dust deposition. • The Berks, Bucks & Oxon Wildlife Trust have advised that further mineral extraction in this area raises serious concerns with regard to indirect impacts on hydrological flows, which the meadows depend on. This will particularly be the case during extraction when the site is actively de-watered and that recent surveys have shown that the SAC meadows are already declining. Landscape / Visual (Policy C8) • Site lies over 5km from an AONB. Water Environment and Flooding • Site does not overlie a source protection zone. (Policy C3 and Policy C4)) • Site overlies a Secondary aquifer. • Site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site lies 150m from an AQMA.

© Adams Hendry Consulting Ltd. 123 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Soil Resources (Policy C6) • Site lies within an area of predominantly Grade 4 and a small part of Grade 3 BMV agricultural land. Historic Environment (Policy C9) • Oxford Canal Conservation Area crosses the site. • Grade II listed Oxford Canal Duke’s Cut Lock lies adjacent to south eastern corner of site. • Site lies within 60m of Grade II listed bridge (east of the site). • Grade II listed Oxford Canal Tilting Bridges 250m south east and 530m north of site. • Grade II listed building 500m to the north west of the site (Mead Farmhouse). • Cluster of listed buildings 750m north west of the site (includes Yarnton Manor and Church of St Bartholomew). • Grade II listed building (Manor Farm) 950m south east of the site and Frieze Farmhouse 1km north east of the site. • Grade II listed Park and Garden (Yarnton Manor) lies 650m north west of the site. • Site lies 900m to the north of a Scheduled Monument (ring ditches, barrows). • Site lies 1.4km from another Scheduled Monument (Godstow Abbey). • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies 5km to the north west of the site. • Historic England have advised that a suitable buffer zone should be provided between the Conservation Area and the working area and that workings should avoid the Grade II listed Duke’s Cut Lock on the Canal, in the south-east corner of the site. Transport and Access (Policy • Site lies adjacent to the A40 on the Oxfordshire lorry route (a through route) C10) • AM and PM peak traffic congestion areas identified in close proximity to site. • Site lies in an area with history of RTIs (7 serious RTIs within 3km of site). • Highways England have advised that clarification should be given as to the proposed access arrangement and would be concerned if any access was proposed onto the Oxfordshire Lorry Route Network without further consultation with the Authority. Public Rights of Way (Policy C11) • Shakespeare recreational route intersects the site. Health and Amenity (Policy C5) • There is a residential dwelling 70m to the east of the site. • Residential dwelling 500m north east of the site and 600m north east of the site. • Residential dwellings at Wolvercote are located 500m south of the site. Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration proposed. Aerodrome Safeguarding (Policy • Site lies within London Oxford Airport buffer of airport safeguarding area. M10)

© Adams Hendry Consulting Ltd. 124 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 3km of three nominated minerals sites: SG-04 Land at Mead Farm, SG-16 Land at Stonehouse Farm and SG-20a Land between Eynsham & Cassington. • The Berks, Bucks & Oxon Wildlife Trust has raised concerns with regards to cumulative and in-combination effects of all relevant projects including other site nominations such as SG-04 (Land at Mead Farm) and SG-16 (Land at Stonehouse Farm, Yarnton) and nearby housing allocations.

Conclusion

The site was nominated in 2009 and there is therefore uncertainty as to whether the site is still available.

The nominated quarry site lies adjacent to the east of the former Cassington Quarry workings. The site lies adjacent to the A40 which may potentially be accessed via an established internal route to the west of the site.

The key constraints which have potential to impact mineral development at the site primarily relate to biodiversity and heritage. The site lies within 100m of the Oxford Meadows SAC and Pixey and Yarnton Meads SSSI which lie to the south of the site, beyond the A40. The site also lies within the Oxford Canal Conservation Area and in close proximity a number of listed buildings. The Shakespeare recreational route also cuts across the site.

Due to the constraints identified above, the site is considered to have limited potential as a mineral working site for sharp sand and gravel and will not be subject to further detailed assessment as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-12: Land South of Chazey Wood

Site Information (as nominated in 2009) Site Location Land South of Chazey Wood

Grid Reference SU 685 752 Administrative Area South Oxfordshire Parish Mapledurham Site Nominee(s) Lafarge Aggregates Limited Proposed Development Sharp sand and gravel extraction. New site (majority of land in arable cultivation). Site Area 51 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield of 3.0 mts (including depth/ Estimated working depth of up to 9.0m overburden) Estimated overburden of up to 3.0m

Proposed Restoration Progressive restoration to water based recreational uses with opportunities to enhance biodiversity. Access No road access proposed. Minerals would be transferred by barge via a cut or a wharf to a processing plant. Estimated Minerals would not be transported Traffic by road. Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within a Mineral Strategic Resource Area or the Mineral Safeguarding Area. Strategy (Policy M3 and C10 • Site located in the southern part of the county (South Oxfordshire). transport) • Site proposed as a potential new quarry. • Estimated total yield is 3.0 mts District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Ancient woodland (Chazey Wood – 28.8ha) lies 95m to the north of the site as confirmed by (Policy C7) the Woodland Trust. Kentwood Grove Ancient Woodland also lies 450m southwest of the site. • A local nature reserve (McIlroy Park) lies 460m south of the site. • Site lies approximately 6.7km to the south east of Hartslock Wood SAC. • Site located in excess of 1km from SSSI, NNR and protected species. Nearest SSSI (Sulham and Tidmarsh Woods and Meadows) is 3.8km west of the site. Landscape / Visual (Policy C8) • Site does not lie within an AONB. However, the Chilterns AONB lies 110m north of the site. • Natural England advise the site is within the setting of an AONB and that consideration will need to be given to inter-visibility between the site and the AONB; where this occurs a Landscape and Visual Impact Assessment will need to be undertaken. Water Environment and Flooding • The site does not lie within a source protection zone. (Policy C3 and Policy C4)) • The site lies within Flood Zone 2 and 3. • Site overlies a principal aquifer. Air Quality (Policy C5) • Site lies adjacent to an AQMA. Soil Resources (Policy C6) • Approximately 60% of the site is Grade 2 and Grade 3 agricultural land with the remainder being Grade 4. Historic Environment (Policy C9) • Grade II* listed Chazey Farmhouse lies 185m to the east of the site, Grade I listed barn lies 245m to the east and Grade II listed Fishery lies 270m to the east of the site - confirmed by Historic England. • Grade II listed New Farmhouse lies 520m west of the site. • Camp on Bozedown Scheduled Monument lies 4.5km northwest of the site. • Grade II listed Prospect Park lies 1.7km south of the site, Grade II* listed Purley Hall lies 2.8km west of the site and Grade II listed Caversham Park lies 3.3km east of the site (Listed Parks and Gardens). • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Historic England advise the potential impact on setting of these heritage assets should be taken into account in deciding whether or not this site, or part of it, is suitable for mineral extraction

© Adams Hendry Consulting Ltd. 128 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Transport and Access (Policy • Site lies 1.6km from the Oxfordshire Lorry Route Network (A4074), however no road access is C10) proposed to the site. • Minerals would be transferred by barge via a cut or a wharf to a processing plant and therefore, the site has potential to enable the transport of minerals by water which is supported by Policy C10. • No AM peak traffic congestion identified within proximity to site. • PM peak traffic congestion on A4074. • No history of serious or fatal RTI’s within 3km of site. Public Rights of Way (Policy C11) • There is a public bridleway within 130m north of the site. Health and Amenity (Policy C5) • Residential dwellings lie adjacent to the south eastern corner of the site. • Cluster of dwellings within 100m east of the site at The Warren. • Dwellings at new Farm lies 520m west of the site. • Residential dwellings in Norcot 150m south of site (opposite side of River Thames). Green Belt (Policy C12) • The site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Potential Cumulative Impact • There are no existing waste sites within 3km of the site: (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site is a potential new quarry. The site currently appears to be in use for agricultural purposes and is within areas of Grade 2 and 3 best and most versatile agricultural land.

The site is not within a Mineral Strategic Resource Area or a Mineral Safegaurding Area and the Chilterns AONB lies 110m north of the site. There may therefore be the potential for inter-visibility between the site and the AONB.

Residential dwellings are in close proximity to the site to the east and in the vicinity (at The Warren). There may also be a potential impact on heritage resources.

For these reasons, the site is not considered to have potential for mineral extraction and will not be subject to further detailed assessment.

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-13: Land at Shillingford

Site Information (as nominated in 2018) Site Location Land at Shillingford Grid Reference SU605930 Administrative Area South Oxfordshire Parish Warborough, Dorchester Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. New quarry. Site Area 295ha Estimated annual 200-300,000 tpa output Estimated Reserves Estimated total yield of 5.3 mts (including depth/ Estimated working depth of 4.53m Estimated overburden of 1.1m overburden) Proposed Restoration Scheme would be designed to minimise risk of bird strike – site falls within safeguarding of 3 Aerodromes. Probable restoration to agricultural land and small waterbodies, reedbed &/or wet woodland within a conservation grassland/ scrub setting. Access Direct access off A4074 - site in three parts, all adjacent to A4074. Possibility to create two new access points. Estimated Unknown Traffic Movements Year of Second half of plan period Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies predominantly within Mineral Strategic Resource Area (Thames, Lower Thame Valley – Strategy (Policy M3 and C10 Oxford to Cholsey) in the southern part of the county (South Oxfordshire). transport) • Site proposed as a potential new quarry. • Estimated total yield is 5.3 mts District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Little Wittenham SAC lies 670m to the south west of the western section of the site and 2km to (Policy C7) the west of the eastern section of the site. • Site located in excess of 500m from a SINC or LNR. Nearest LNR is 2.5km east of site. • Ancient Woodland within 15m north eastern section of site (Ladybrook Copse) and 670m southwest of the western section of the site (Little Wittenham Wood). • Little Wittenham SSSI lies 700m southwest of the site. • Phase 2 North Farm River of Life Project 2013/14 (Priority Habitat Creation and Restoration) lies 250m south of the western section of the site. • Site located in excess of 5km from SPAs, Ramsar Sites, NNRs, Local Wildlife Sites and Local Geological Sites. Landscape / Visual (Policy C8) • Site lies within 150m of North Wessex Downs AONB. • Natural England note in their consultation response that consideration will need to be given to inter-visibility between the site and the North Wessex Downs AONB. Water Environment and Flooding • Site does not lie within a source protection area. (Policy C3 and Policy C4)) • Site lies within Flood Zones 2 and 3. • Site lies within a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies within Grade 1 and 2 agricultural land. Historic Environment (Policy C9) • Site lies adjacent to conservation area in Warborough. • Grade II listed milestones adjacent to eastern and western section of the site on A4074. • Scheduled monuments lie 65m north of the site (ring ditches, cursus, enclosures and settlement site), 375m west of the site (Roman Town) and 460m to the west of the site (Dike Hills). • Listed buildings at Overy lie 100m from the western section of the site. • There are also Grade II listed buildings at Shilingford and Warborough between the two sections of the site, the nearest being 85m from either site boundary. • Battlefield 4.4km north east of the site. • Grade II listed Parks and Gardens lie 3.7km north of site (Ascott Park) and 4.2km north west of site (Nuneham Courtenay).

© Adams Hendry Consulting Ltd. 133 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies in excess of 5km from any World Heritage Sites. • Historic England note that, the eastern area of Site SG-13 contains a Scheduled Monument (the Romano-British settlement 520m north west of Cooks Cottages) and is within the setting of the Warborough Conservation Area. The central area is within the setting of another Scheduled Monument (Ring ditches, cursus, enclosures and settlement site) and the western area is within the setting of the Overy Conservation Area and a number of listed buildings. Transport and Access (Policy • Site lies adjacent to A4074 Oxfordshire Lorry Route access. C10) • Site lies adjacent to A4074 where there is history of 2 serious RTIs. • PM peak traffic congestion identified within proximity to the site. Public Rights of Way (Policy C11) • Thames Path lies within 200m of the southern boundary of the site. Health and Amenity (Policy C5) • Dwellings on The Green S and The Green N, Warborough lie adjacent to the north western boundary of the eastern section of the site. • Residential dwellings in Shillingford adjoin the site and dwellings in Warborough are also situated between the two sections of the site. • There are also properties at Overy 100m to the west and at Benson 350m to the east. Green Belt (Policy C12) • The site lies within the Green Belt Aerodrome Safeguarding (Policy • The site lies within the Dalton Barracks, RAF Calgrove and RAF Benson Aerodrome M10) Safeguarding area.

Potential Cumulative Impact • Site lies within 3km of three existing waste sites: Oakley Wood, Benson STW and Battle Farm. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of two nominated waste sites: 225 Cedars Storage and 286 Wally Corner. • Site lies within 3km of two nominated minerals sites: SG-03 Land adjacent to Benson Marina and SG-09 Land north of Drayton St Leonard and Berinsfield and land at Stadhampton.

Conclusion

The site is proposed as a new quarry which primarily lies within a MSRA and lies adjacent to the A4074 Oxfordshire Lorry Route.

There are however a number of constraints to the working of minerals at this site including potential impacts on the Little Wittenham SAC, loss of best and most versatile agricultural land, impacts on the historic environment (in particular the setting of the Warborough and Overy Conservation Areas) and the numerous residential receptors located adjacent to and in very close proximity to the site. The site is also in the Green Belt and within close proximity to the AONB.

For these reasons, the site will not be considered further for potential sand and gravel extraction.

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-15: Dairy Farm (including SG-58 and SG-58a)

Site Information (as nominated in 2018) Site Location Dairy Farm (including SG-58 and SG-58a) Grid Reference SP 302 014 Administrative Area West Oxfordshire Parish Clanfield, Black Bourton Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. New quarry. Site Area Total area: 558.2ha SG-15 approx. 228 ha SG-58 approx. 111 ha Estimated annual Up to 450,000 tpa output Estimated Reserves SG-15: Estimated total yield of 5.4 (including depth/ mts Estimated working depth of 4.25m overburden) Estimated overburden of 0.5m

SG-58: Estimated total yield of 5.06 mts Estimated working depth of 3.9m Estimated overburden of 0.7m

SG-58a: Estimated total yield of 12 mts Estimated working depth of 5.88m Estimated overburden of 0.6m Proposed Restoration Mixture of agricultural land, open water & reedbed/wet woodland – extent of open water likely to be limited due to proximity of Brize Norton airfield. Recreational afteruses could be linked with the R.

Access SG-15: Direct access to A4095. Potential opportunity for sustainable transport via River Thames. SG-58 and SG-58a have direct access to B4020. Estimated Unknown Traffic Movements Year of Second half of plan period Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • The site(s) are outside the Minerals Strategic Resource Area (MSRA) but SG-58 and SG-58a Strategy – Strategic Resource lie within the Minerals Safeguarding Area. Areas (Policy M3) • Site located in the northern part of the county (West Oxfordshire). • Potential new quarry. • Estimated site yield, for all three sites, is 5.4mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. (Policy C7) • Areas of Ancient Woodland 570m and 900m south of SG-58 and 800m north of SG-58a. • Site does not lie within 1km of LNR or NNR. • Alvescot Meadows SSSI 1km north of SG-58a • Local wildlife site or Local Geological site do not lie within 500m of the site. • Great Brook Habitat Improvement Project (Priority Habitat Creation and Restoration) adjoins south eastern corner of site. Rushey Lock Fish Bypass Channel and Radcot Lock Fish Bypass Project are both within 400m of the south of the site. Landscape / Visual (Policy C8) • Site lies over 3km from any AONB.

© Adams Hendry Consulting Ltd. 138 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Water Environment and Flooding • There is an area of Flood Zone 2 and 3 to the south of the site and an area of Flood Zone 3 to (Policy C3 and Policy C4)) the north of the Site. • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 2 and 3 agricultural land (evenly split). • There is a comparatively small area of Grade 4 agricultural land to the south of the Site along the River Thames. Historic Environment (Policy C9) • A Scheduled Monument (Burroway Enclosure) is within SG-15. A further Iron Age Settlement also a Scheduled Monument is located partially within SG-58a. • Scheduled Monuments also 120m west of SG-58 and 160m south of SG-15. • The Golden Ball, Grade II Listed Building lies adjacent to the southeast boundary of SG-58 and the south west boundary of SG- 58a to the north of Clanfield. • There are numerous listed buildings in Clanfield, which are within 250m of the Site. • Site lies within 500m of a Conservation Area. • Site lies in excess of 5km from any battlefields or World Heritage Sites. • Buckland House (Grade II* listed Park and Garden) lies 2.2km south east of the site. • Historic England advised that the nearby Burroway Enclosure archaeological remains may extend beyond the scheduled area and further detailed assessment should be carried out, they therefore advise that site SG-15 be excluded from the overall site area. Transport and Access (Policy • Site areas SG-15 and SG-58a are adjacent to the A4095, a local access route on the C10) Oxfordshire lorry route network. Site SG-58 and SG-58a can be accessed from the B4020, also a local access route. • Potential opportunity for transport via River Thames via SG-15. • The site(s) are over 10km to the A40 (through route) to the north. Access to the south through the village of Clanfield is not suitable. • Site is likely to impact on PM traffic congestion along the A4095 and roads around Brampton. • There are two RTI histories within 2km of the site, one ‘serious’ and one ‘fatal’. Public Rights of Way (Policy C11) • There are FPs within the west area, linking Mill House and Bazeland Farm; the central north area linking Clanfield and Alvescot; and a FP linking Merlin House with the Clanfield Road adjacent to the east boundary of the Site. • There are a number of footpaths which cross through the southern half of the site (SG-15) and one which follows the Thames along the southern site boundary. Health and Amenity (Policy C5) • Dwellings adjoin the southern and north eastern boundaries of SG-58a. • The site(s) boundary is adjacent to the village of Clanfield, surrounding the village to the west, north and east, in close proximity to residential properties. • Small clusters of residential dwellings including Merlin House, Garth House, Bazeland Farm and Mill Farm and dwellings at Black Bourton and Alvescot are within close proximity to the north of the site.

© Adams Hendry Consulting Ltd. 139 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton Aerodrome Safeguarding area. M10)

Potential Cumulative Impact • There is one existing waste sites within 3km of the site: Elmwood Farm. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of three nominated waste sites: 003 Dix Pit, 103 Land at Lakeside Industrial Estate and 236 Sheehan Recycled Aggregates • Site lies within 3km of two mineral sites: SG58 and SG58a.

Conclusion

The site(s) is proposed as a new quarry site. The site(s) lies outside of the MSRA but is predominantly within the Minerals Safeguarding Area.

Access to the site(s) would be via the A4095 or B4020 both local access roads on the Oxfordshire Lorry route network.

The site(s) surrounds the village of Clanfield to the west, north and east. The key constraints which have potential to impact mineral development at the site primarily relate to potential adverse effects on residential amenity and the historic environment.

For these reasons, the site will not be taken forward for further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-16: Land at Stonehouse Farm

Site Information (as nominated in 2018) Site Location Land at Stonehouse Farm Grid Reference SP 483 114 Administrative Area Cherwell Parish Yarnton Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. Extension to Cassington Quarry. Site Area 35 ha Estimated annual output Unknown

Estimated Reserves Estimated total yield of 1.12 mts (including depth/ Estimated working depth of 3.37m Estimated overburden of 0.97m overburden) Proposed Restoration Low-level agricultural use and wetland. Also, possible to return the northern part of the site to be suitable for residential use, with southern area as wetland. Access Vehicular access possible off Cassington Road (near to Oxford Industrial Park) – sufficient space is available to create a one-way access & exit with visibility in excess of the minimum guidelines in Manual for Streets. Estimated Traffic Estimated 50 trips by 20t lorry per Movements day which, using typical working day of 7 hours, results in an extra 14 vehicular trips per hour on the highway network. There is now an opportunity to use jet pumping to transport mineral to Cassington for processing – using

© Adams Hendry Consulting Ltd. 142 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 an existing tunnel under the railway. Alternatively, it may be possible to conveyor material to the Cassington Quarry for processing – subject to feasibility study e.g. of crossing railway Year of Not before 2021 Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

© Adams Hendry Consulting Ltd. 143 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Air Quality (Policy C5) • Site within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 4 agricultural land. • Restoration proposed. Historic Environment (Policy C9) • Site lies within 200m of Grade II listed buildings (west of the site). • Site adjacent to the Oxford Canal Conservation Area. • Site lies 1.4km from a Scheduled Monument (ring ditches, barrows). • Site lies 1.8km from another Scheduled Monument (Godstow Abbey). • Site lies within 4.3km of a World Heritage Site and Grade I listed Park and Garden (Blenheim Palace). • Yarnton Manor (Grade II listed Park and Garden) lies 250m west of the site. • Site lies in excess of 5km from any battlefields. Transport and Access (Policy • Site lies within 300m of the A44 on the Oxfordshire lorry network via Cassington Lane. C10) • There may be an opportunity to transport land-won material from this site to the existing processing plant to the south of the adjacent railway line either through an existing tunnel, or via a conveyor system over the existing railway line. The access to the Oxfordshire Lorry route Network would then be via the established access onto the A40 to the south. • AM and PM peak traffic congestion areas identified in close proximity to site. • Site does not lie in close proximity to an area with history of RTIs. Public Rights of Way (Policy C11) • Several footpaths cross the northern section of the site plus one along the western boundary which forms part of Shakespeare’s Way. • Some temporary path diversions likely to be required. Health and Amenity (Policy C5) • Nearest residential dwellings 15m to the north of the site off Cassington Road and 100m to the east off the A44. Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within London Oxford Airport buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of two existing waste sites: Worton Farm and Charlett Tyre Yard. (minerals and waste sites) • Site lies within 3km of one existing minerals site: Cassington Quarry. • Site lies within 3km of two nominated waste sites: 009 Worton Farm (Areas C & D) and 261 The Marshes. • Site lies within 3km of three nominated minerals sites: SG-04 Land at Mead Farm, Yarnton, SG-05 Land to the East of Cassington Quarry and SG-20a Wharf Farm, Cassington.

Conclusion

The site is a potential extension to an existing quarry that appears to be in use for agricultural purposes. The site is within the Green Belt and is outside the

The site lies within close proximity to the Oxford Meadows SAC/SSSI. Further detailed assessments would need to be undertaken to determine whether extraction could take place here whilst avoiding significant impacts on the SAC/SSSI.

For these reasons, the site is considered to have limited potential as a mineral working site for sharp sand and gravel and will not be and subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-36 – Land at Friars Farm

Site Information (as nominated in 2009) Site Location Land at Friars Farm

Grid Reference SP 406 065

Administrative Area West Oxfordshire

Parish Stanton Harcourt and South Leigh

Site Nominee(s) Lakeside Industrial Estate

Proposed Development Sharp sand and gravel extraction. New quarry.

Site Area 3 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield of 0.4 mts. (including depth/ Estimated working depth of up to 3.5m overburden) Estimated overburden of 0.3-1.4m Proposed Restoration Low level agriculture

Access Access off roundabout onto B4449

Estimated Unknown Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies outside Mineral Strategic Resource Area and does not lie within the Mineral Strategy – Strategic Resource Safeguarding Area. Areas (Policy M3) • The site lies within the northern part of the County (West Oxfordshire). • Potential new quarry. • Estimated total yield of 400,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. Nearest SAC (Oxford (Policy C7) Meadows) is 6.4km northeast of the site. • Tar Wood (Ancient Woodland) lies 260m northeast of the site. • Site lies within 1.1km of the Stanton Harcourt SSSI located to the southeast of the Site. • Church Mill Fish Pass (Priority Habitat Creation and Restoration point) lies 2.5km south of the site. • Dix Pit Proposed Local Wildlife Site Extension lies 760m south of the site. • Devils Quoits Local Geological Site lies 1.3km south of the site. • Site does not lie in close proximity to any LNR’s or NNR’s. Landscape / Visual (Policy C8) • Site lies in excess of 3km of any AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site does not lie within Flood Zones 2 or 3. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 2 agricultural land. Historic Environment (Policy C9) • Site lies adjacent to the Stanton Harcourt and Sutton Conservation Area. • Listed building 460m east of the site. Listed buildings in Stanton Harcourt 520m southeast of the site and 640m east of the site in Sutton. The Old Vicarage (Grade II listed) lies 470m south of the site. • There are numerous Listed buildings at Stanton Harcourt and Sutton located within 1km of the Site. • The Devil’s Quoits Scheduled Monument lies 1.3km south of the site and another Scheduled Monument (sites near Foxley Farm) lies 1.6km northeast of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 3.7km north of the site. • Site lies in excess of 5km from any battlefields or World Heritage Sites.

© Adams Hendry Consulting Ltd. 148 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Transport and Access (Policy • The site is on the Oxfordshire Lorry Route. The B4449 is identified as a local access route and C10) is approximately 4km from the A415 also a local access route and approximately 5km from the A40 through route. • The B449 goes through the village of Sutton Green approximately 500m from the B449 roundabout. • There are no ‘serious’ or ‘fatal’ RTI histories within 3km of the Site. • Site traffic may impact on AM and PM congestion along the A415 South of Standlake. Public Rights of Way (Policy C11) • There is a foot path which links Tarwood with Stanton Harcourt. This crosses the south of the Site from west to east. • There is a second foot path which follows the Site access track from Eynsham Road and follows the east boundary of the site north to Stanton Harcourt Road. Health and Amenity (Policy C5) • There is a residential property at, Burys Farm, adjacent to the northeast corner of the site. • Properties in Sutton and Stanton Harcourt lie approximately 350m east of site and properties on Cogges Lane lie 500m southwest of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton, London Oxford Airport and Dalton Barracks M10) Aerodrome Safeguarding areas.

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Rear of Cemex Batching Plant, Dix Pit and Controlled Reclamation. (minerals and waste sites) • Site lies within 3km of 2 existing minerals sites: Gill Mill Quarry and Stanton Harcourt Quarry (Stonehenge Farm). • Site lies within 3km of 3 nominated waste sites: 003 Dix Pit, 103 Land at Lakeside Industrial Estate and 236 Sheehan Recycled Aggregates. • Site lies within 3km of 5 nominated minerals sites: SG-27 Vicarage Pit, Cogges Lane, SG-28 Guy Lakes North, SG- 29 Sutton Farm, Sutton, SG-30 Home Farm, Brighthampton and SG-31 Land East of Sutton.

Conclusion

The site is proposed as a relatively small, new quarry. The site lies outside of the MSRA and the Minerals Safeguarding Area in the north part of the County. The site would be accessed via a local access route and is approximately 5km to A40 strategic through route. The village of Sutton Green is located on the B4449 in close proximity to the site.

There are other constraints to mineral working including the site’s proximity to the Stanton Harcourt SSSI, the conservation areas in Stanton Harcourt and Sutton Conservation Area and Grade 2 BMV agricultural land. Potential Cumulative impacts would also need to be considered further.

For these reasons, the site will not be taken forward for further detailed assessment.

Take forward for detailed assessment Not taken forward for detailed assessment

SG-37: Land at Grandpont and South Hinksey

Site Information (as nominated in 2009) Site Location Land at Grandpont and South Hinksey Grid Reference SP 510 050 Administrative Area Oxford City Council Parish Oxford, North Hinksey Site Nominee(s) Grandpont Waters Proposed Development Sharp sand and gravel extraction. New site. Site Area 20ha Estimated annual Unknown output Estimated Reserves Estimated total yield of 1.5 mts. (including depth/ Estimated working depth and overburden unknown overburden) Proposed Restoration Construction of an 85m wide, 1800m long watercourse for canoeing, rowing and other water sport activities. Also 2 x 90 berth pleasure and narrow boat marinas, a network of paths, cycleways and wildlife lakes. Access Existing access appears to be onto Old Abingdon Road (within 300m of A423) Estimated To be assessed Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within the Mineral Strategic Resource Area or Mineral Safeguarding Area. Strategy – Strategic Resource • Site is located in the centre of the County (Oxford City Council). Areas (Policy M3) • Site proposed as a potential new quarry. • Estimated total yield of 1.5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies within a Priority Habitat Creation and Restoration area. Two further Priority Habitat (Policy C7) Creation and Restoration points lie 700m north of the site and 800m east of the site (Hinksey Fish Pass). • Site lies adjacent to a Local Wildlife Site (Hinksey Lake) which is east of the railway. • Oxford Meadows SAC lies approximately 1.8km to the north and Cothill Fern SAC lies approximately 5.3km to the south west. • Site lies within 440m of a SSSI (Iffley Meadows) to the south-east. Site lies within 1.5km of Magdalen Grove SSSI to the north east and within 1.7km of another SSSI to the north (Port Meadow with Wolvercote Common & Green). • Ancient woodland lies 560m south of the site (Bagley Wood) and also 800m east of the site. • Lye Valley Local Nature Reserve lies 3.9km east of the site. • Site does not lie in close proximity to any NNR’s. • Lye Valley Local Geological Site lies 3.6km to the east of the site. • The EA advise that the majority of this site is identified as part of the Oxford Flood Alleviation Scheme. The site has been identified as a suitable area for environmental mitigation as part of this scheme to provide habitat replacement for biodiversity. Landscape / Visual (Policy C8) • Site lies over 3km from an AONB. Water Environment and Flooding • Site does not within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a Secondary Aquifer. • Site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site lies within an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • A Grade II listed memorial lies adjacent to the north-eastern corner of the site. • Listed buildings in North Hinksey Village lie 50m west of the site. • Site also lies within 350m of numerous listed buildings in Oxford, to the northeast. • Listed Parks and Gardens lie 675m east of the site (Christ Church – Grade I) and 770m north of the site (Worcester College – Grade II*).

© Adams Hendry Consulting Ltd. 153 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Scheduled Monuments lie 550m northeast of the site (Oxford Castle) and 730m north of the site (Rewley Abbey). • Site lies in excess of 5km from any battlefields or World Heritage Sites. Transport and Access (Policy • Site lies within 250m of the Oxfordshire Lorry Route Network (A423). C10) • The access road included as part of the site is in use as Network Rail access to Hinksey Yard rail depot. • Areas with AM and PM peak traffic congestion identified within proximity to site. • Site lies within proximity of areas with history of serious and fatal RTIs Public Rights of Way (Policy C11) • Public footpath crosses the access road into the site. Health and Amenity (Policy C5) • Residential dwellings in North Hinksey village lie 45m to the west of the site. • Dwellings in Gibbs Crescent lie 150m north of the site. • Dwellings in New Hinksey lie 100m to the east and dwellings in Oxford lie 200m to the north east of the site. Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport and Dalton Barracks buffers of airport safeguarding. M10)

Potential Cumulative Impact • There are no existing waste sites within 3km of the site. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site was nominated in 2009, there is therefore uncertainty as to whether the site is still available.

The site is outside the Mineral Strategic Resource Area and the Mineral Safeguarding Area and is located in the Green Belt. It is also within an Air Quality Management Area.

Mineral working has the potential to give rise to adverse effects on biodiversity given the site’s proximity to designed sites.

The Environment Agency advise that the majority of this site is identified as part of the Oxford Flood Alleviation Scheme. The site has been identified as a suitable area for environmental mitigation as part of this scheme to provide habitat replacement for biodiversity.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-41: North of Lower Radley

Site Information (as nominated in 2009) Site Location North of Lower Radley

Grid Reference SU532997

Administrative Area Vale of White Horse Parish Radley Site Nominee(s) FTMINS

Proposed Development Sharp sand and gravel extraction. New quarry.

Site Area 56.58 ha

Estimated annual 150,000 tpa output Estimated Reserves 1.5 million tonnes (including depth/ Average depth of 3m Average overburden of 1.5m overburden) Proposed Restoration Phased restoration scheme to achieve an afteruse of leisure related nature conservation and biodiversity uses. Access Likely to be via a staithe/wharf onto the River Thames. Estimated Unknown. Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Thame Valley – Oxford to Strategy – Strategic Resource Cholsey) in the southern part of the county (Vale of White Horse). Areas (Policy M3) • Site is proposed as a new quarry. • Estimated site yield is 1.5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Ancient Woodland lies 200m to the west of the site (North Close Copse). (Policy C7) • Radley Gravel Pits Proposed Local Wildlife Site Extension lies 500m south of the site. • Site lies within 1.7km of a SSSI to the north west. • Cothill Fen SAC lies 6.2km to the west and the Little Wittenham SAC lies approximately 6.3km to the south-south east. • Site lies within 2km of a Local Nature reserve to the south west. • Cothill NNR lies 6.6km west of the site. • Priority Habitat Creation and Restoration at Sandford lies 1.1km north of the site. • Dry Sandford Quarries Local Geological Site lies 5.8km to the west. • The Berks, Bucks and Oxon Wildlife Trust advise that quarrying at SG-41 might adversely affect a lowland meadow priority habitat that is immediately south to the site. They also advise that the site should be considered sensitive in ecological terms. Landscape / Visual (Policy C8) • Site lies over 3km from an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. • Site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site lies 1.5km from an AQMA. Soil Resources (Policy C6) • Site lies within an area of primarily Grade 4 agricultural land with a small areas of Grade 2 BMV. • Restoration potential. Historic Environment (Policy C9) • Site lies within 225m north of a Registered Historic Grade I listed Park and Garden (Nuneham Courtenay). • Historic England have acknowledged that the site does not include the Nuneham Courtenay conservation area but advise that site should avoid these areas and consideration be paid to the setting of this asset. • Site lies within 60m of Grade II listed properties in Lower Radley. • Site lies within 850m north of a Scheduled Monument (Settlement Site) and within 1.2km from another Settlement Site to the west.

© Adams Hendry Consulting Ltd. 158 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 300m from a Conservation Area to the west of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. Transport and Access (Policy • Site access via road would be via the single-track Lower Radley. C10) • Site lies within 3.5km of the Oxfordshire Lorry Route Network (A4183) • Site does not lie in close proximity to an area with history of RTIs. • No AM or PM peak traffic congestion areas identified within proximity to site. • Feasibility of site access via a staithe/wharf onto the River Thames would require further assessment. Public Rights of Way (Policy C11) • Public footpath within the site and the Thames Path runs along the eastern boundary adjoining the River Thames. • Appropriate agreed temporary diversions and potential for establishment of fresh permissive occasional footpath and track. Health and Amenity (Policy C5) • Nearest residential dwellings 90m south of the site in Lower Radley. Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration proposed. Aerodrome Safeguarding (Policy • Site lies within the Dalton Barracks buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Culham JET, The Metal Yard Nuneham Courtenay and Oxford STW. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of 2 nominated waste sites: Culham No.4 Site and Thrupp Lane Radley. • Site lies within 3km of 2 nominated minerals sites: PFA-01 Land at Thrupp Lane, Radley and SG-42 Nuneham Courtenay.

Conclusion

The site was nominated in 2009 and its current availability is unknown.

The site is constrained to the west by a railway line running north to south, access by road is therefore challenging with limited opportunities. The likely connection via road is through Lower Radley to the south. However, this road appears unsuitable for the movement of large goods vehicles due to on- street parking arrangement, residential properties aligning the route and restrictions on vehicles over 7.5t. The Oxfordshire Lorry Route Network (A4183) lies approximately 3.5km to the west of the site via this route.

There is however the potential to transport material via wharf onto the River Thames, which is identified as a potential method by the site promotor. However, the Thames Path, a national Trail, runs adjacent along the western bank of the River Thames. This option would therefore likely prejudice the integrity of this route.

© Adams Hendry Consulting Ltd. 159 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Although the site lies within the Mineral Strategic Resource Area, it is also in the Green Belt. Whilst there is a demonstrable opportunity to transport excavated material sustainably by water, due to the potential adverse impact on the Thames Path and poor alternative transport connections by road, the site has limited potential for mineral development and would not be considered further as part of this process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SG-61: Mains Motors

Site Information (as nominated in 2008) Site Location Mains Motors, Ewelme

Grid Reference SU648893

Administrative Area South Oxfordshire

Parish Benson

Site Nominee(s) Mains Motors Ltd

Proposed Development Sharp sand and gravel extraction. New quarry. Site Area 10 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield is unknown (including depth/ Estimated working depth and overburden also unknown. overburden) Proposed Restoration Recycling as present.

Access Existing access onto Old London Road (within 1km of A4130)

Estimated Unknown Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within the Mineral Strategic Resource Area or within the Mineral Safeguarding Strategy – Strategic Resource Area. Areas (Policy M3) • Site is located in the southern part of the county (South Oxfordshire). • Site proposed as a potential new quarry. • Estimated total yield is unknown. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • The Woodland Trust advises that the site forms the north, west and part of the south boundary (Policy C7) of Ancient Woodland (AW) Mogpits Wood (5.3ha) and is also adjacent to small boundary of AW Oakley Wood (7.6ha). • Site located in excess of 1km from SSSI, NNR and protected species. • SSSI lies 2.5km to the northeast of the site. • Little Wittenham SAC lies approximately 8.2km to the north west of the site. • Site located in excess of 500m from a SINC or LNR. • Ewelme Watercress Beds Local Nature Reserve lies 2km north of the site. • Mongewell Woods Proposed Local Wildlife Site lies 2km south of the site. Landscape / Visual (Policy C8) • Site lies within the Chilterns AONB. Water Environment and Flooding • Site overlies a principal and secondary aquifer. (Policy C3 and Policy C4)) • Site does not lie within Flood Zone 2 or 3 or a source protection zone. Air Quality (Policy C5) • Site not located within 1km of AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There is a single listed building at Gould’s Grove Farm 350m to the north west. • Scheduled Monument (Site of Manor House and Royal Palace) lies 1.8km north of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Fairmile Hospital Grade II listed Park and Garden lies 5.4km southwest of the site. • Grade II listed building lies 400m northwest of the site. Transport and Access (Policy • Access to the Oxfordshire Lorry Route Network (A4130) from the site is via Old London Road. C10) A4130 is approximately 1km from the site. • There is a cluster of residential properties at the junction with the A4130. • No AM or PM peak traffic congestion identified within proximity to the site. • The site lies within close proximity to an area with history of RTI’s. Public Rights of Way (Policy C11) • There is a public right of way adjacent to the west boundary and a second public right of way adjacent to the east boundary.

© Adams Hendry Consulting Ltd. 163 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • There is one residential property approximately 160m to the north west of the site and a second cluster of three houses 225m to the east. • Dwellings at Gould’s Grove Farm lie 400m to the northwest of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Chalgrove buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 6 existing waste sites: Battle Farm, Oakley Wood, Ewelme no 1, Ewelme no 2 and (minerals and waste sites) Rumbold’s Pit, Eyres Lane. • There are no existing minerals sites within 3km of the site. • Site lies within 3km of 4 nominated waste sites: Ewelme No. 2 Site, Woodside, Old Henley Rd, Ewelme No. 1 Site and Ambrose Quarry. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site currently operates as an MRS/ELV site within the Chilterns AONB. The site nomination is from 2009 and it is not known whether the site remains available.

The site does not lie within the Mineral Strategic Resource Area or within the Mineral Safeguarding Area.

A number of other constraints restrict the potential use of the site for mineral extraction including its proximity to ancient woodland and its location, overlying principal and secondary aquifers.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site SS-17: Land north and south of A420 near Fyfield and Tubney

Site Information (as nominated in 2018) Site Location Land north and south of A420 near Fyfield and Tubney Grid Reference SU432992 (land north of A420) and SU441993 (land south of A420) Administrative Area Vale of White Horse Parish Fyfield and Tubney

Site Nominee(s) Hills Quarry Products Ltd

Proposed Development Soft sand extraction. New quarry. Site Area 46 ha

Estimated annual 100,000 tpa output Estimated Reserves Estimated total yield of 2 mts (including depth/ Estimated working depth of 5m (tbc) Estimated overburden of 0.3m overburden) Proposed Restoration Agriculture

Access Existing access onto A420, but new access points onto A420 are proposed. Estimated TBC Traffic Movements Year of Upon grant of Planning Permission. Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Corallian Ridge – Oxford to Strategy – Strategic Resource Faringdon) in the southern part of the county (Vale of White Horse). Areas (Policy M3) • Site is proposed as a potential new quarry. • Site lies adjacent to A420. • Estimated total yield is 2.0 mts District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • The southern part of the site (south of the A420) is adjacent to Frilford Heath, Ponds and (Policy C7) Fens SSSI. Appleton Lower Common SSSI lies approximately 1km to the north • Ancient woodland borders the site to the north, south and east (Church Copse to the south, Appleton Upper Common to the north and Tubney Wood to the east). • Cothill Fen SAC is approximately 1.4km east of the site. • The Berks, Bucks and Oxon Wildlife Trust comment that the site is also located within the Oxford Heights West Conservation Target Area. Landscape / Visual (Policy C8) • The site does not lie within 3km of an AONB Water Environment and Flooding • The northern boundary of the site adjoins a watercourse and is within flood zone 3 with the (Policy C3 and Policy C4) remainder of the site in flood zone 1. • The site does not appear to lie within a source protection zone or overlie an aquifer. Air Quality (Policy C5) • The site does not lie within 1km of an AQMA. Soil Resources (Policy C6) • The site is predominantly Grade 2 agricultural land, with a small part on the northern boundary in Grade 3. Historic Environment (Policy C9) • Grade II listed barn adjacent to site south of the A420. Tubney Warren House and attached walls is located approximately 25m away. • There is a cluster of three Grade II listed buildings north of the A420, including the Church of St Lawrence approximately 70m from the boundary of the site. • There are also listed buildings in Tubney within 250m of the site to the south and a number of listed buildings in Fyfield approximately 700m to the west of the site. • The boundaries of the Fyfield Conservation Area and Netherton Conservation Area lie (approximately 500m and 750m respectively) to the west of the site. Transport and Access (Policy • Site lies adjacent to the A420 on the Oxfordshire Lorry Route Network. C10) • No AM peak or PM peak traffic congestion areas identified within proximity to site. Public Rights of Way (Policy C11) • A public footpath runs north south from Netherton Road to the A420 through the eastern part of the site. There is another footpath running south from the A420 in close proximity to the site.

© Adams Hendry Consulting Ltd. 167 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • Residential dwellings lie adjacent to the site. Green Belt (Policy C12) • The site lies within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the Dalton Barracks airport safeguarding zone. M10)

Potential Cumulative Impact • Site lies within 3km of no existing waste sites. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Upwood Quarry. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of 1 nominated minerals site: SS-05.

Conclusion

The site has been nominated as a potential new quarry site within the Mineral Strategic Resource Area. It overlies an area of best and most versatile agricultural land.

The site lies adjacent to a SSSI, ancient woodland and in close proximity to a number of listed buildings. Natural England advise that potential impacts include changes in hydrology, air pollution from traffic and dust deposition. Consideration will also need to be given for potential effects on the hydrology of Cothill SAC in-combination with the existing Upwood Park Quarry.

Based on the constraints identified as part of this initial screening assessment, the site is considered to have limited potential for mineral development and would not be considered further as part of this assessment process.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site 002: Prospect Farm, Chilton

Site Information (as nominated in 2018) Site Location Prospect Farm, Chilton

Grid Reference SU 497 847

Administrative Area Vale of White Horse

Parish Upton

4Site Nominee(s) Raymond Brown Minerals & Recycling Ltd Proposed Permanent retention of existing Development temporary recycling facility for inert and non-hazardous waste Site Area 1.2 ha Existing Capacity 50,000 tpa. Annual Throughput 35,797 tpa (2017) 39,126 tpa (2016) 30,603 tpa (2015) Existing land use Existing recycling facility for inert and non hazardous waste – time limited permission to 31.12.2022

Access Existing access (over 1km from A34) Current levels and 54 movements per day into and out of types of traffic site for ‘waste in’ (HGV skip vehicles & movement a very small number of vans). Approx. 7 vehicles per day for ‘materials out’ (bulker lorries, tipper lorries and a very small number of vans)

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is an existing site with capacity to processes approximately 50,000 tpa and is currently (Policy W4) considered to be a strategic waste management facility in accordance with Policy W4. • The site lies within 5km of Didcot. • Site lies 1.5km from access onto the Oxfordshire lorry route network (A34). • Site is an established existing waste site with suitable existing access arrangements. • Site does not lie within 200m of a SAC. • Site lies within North Wessex Downs AONB.

District Local Plan Allocation • Site does not conflict with a District Local Plan Allocation. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. (Policy C7) • Site does not lie within or adjacent to ancient woodland. • Site does not lie within 1km of SSSI, NNR. • Comments made by Natural England at the Issues and Options Consultation (Rep No. 144) include: “The site is adjacent to a Local Wildlife Site supporting calcareous grassland” Landscape / Visual (Policy C8) • Site lies within AONB (North Wessex Downs). Water Environment and Flooding • Site does not lie within a flood zone 2 or 3. (Policy C3 and Policy C4) • Site does not lie within source protection zone. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 2 agricultural land, although site has previously been developed.

Historic Environment (Policy C9) • No impact on historic environment. There are currently no known archaeological constraints.

Transport and Access (Policy C10) • Site does not lie in close proximity to an area with history of RTIs. • No AM peak or PM peak traffic congestion identified within proximity to site. • Poor access to public transport connections. • West Berkshire Council advise that the site is close to the West Berkshire Boundary. It is likely that some traffic from the site could travel south into West Berkshire and wider, cross boundary traffic impacts would need to be considered should the site be considered for allocation.”

Public Rights of Way (Policy C11) • This site has a large number of footpaths, bridleways, restricted byways and byways in the immediate surrounds. Current waste uses at the site do affect PRoW users due the proximity of the network to the haul traffic access routes. Some local conflict already exists with vehicles using the wrong routes for access. Improvements would be required to signage. • However, this is likely to be contrary to aims of the AONB Management Plan in terms of loss of tranquillity and reduction in amenity for people using the area.

Health and Amenity (Policy C5) • Residential dwelling lies within 1km to the north-west of the site, although does not align route likely to be used for site access. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • There are no existing waste or minerals sites within 3km of the site. waste sites) • Site lies within 3km of a nominated waste site: 285 (Magnox) Harwell Site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site is an existing waste recycling facility. The primary constraint to this site is its location within the North Wessex Downs AONB. However, the site is well screened by planting and bunds on its perimeter boundary which reduces its impact on the AONB.

The site lies within close proximity to the Didcot urban area and may therefore suitable to provide small-scale, non-strategic and strategic waste management capacity in accordance with Policy W4. The site lies 1.5km from access onto the Oxfordshire Lorry Route Network (A34). However the approach to the A34 is entirely via a secluded access route used only by the existing waste site and neighboring agricultural uses.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 002 Site Name: Prospect Farm, Chilton

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

Site currently has temporary permission for a Waste Transfer Station with a capacity of 50,000tpa (planning permission MW.0127/09 dated 29th October 2009)

It has an end date of 2022 with restoration to be complete by 31st August 2023.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and as previously developed land is in compliance with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known records of Irreplaceable Habitats, Notable Habitats or European Protected species within or adjacent to the site.

Records indicate badger presence within area. Records for bird species including turtle dove and yellowhammer.

The site is adjacent to Chilton Disused Railway Line Local Wildlife Site (LWS) (lowland calcareous grassland). Any anticipated further impacts on LWS must be minimised and appropriate mitigation measures provided for the site’s restoration and to the benefit of biodiversity.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site itself is well screened. Operational areas are limited to pockets within the site boundary. The surrounding landscape context comprises

characteristic large agricultural fields with low/no hedgerows. There is a great sense of openness.

There are several PRoWs within the area. Whilst the site is screened, there may be occasional views from selected footpaths, roads and houses. Noise and activity (including HGV movements) also influence views and perception.

No impact on historic landscape character anticipated.

The extant consent for waste uses on this site is temporary and requires the restoration of the site by 2022. On this basis, the potential allocation of the site for waste uses within the AONB is likely to potentially result in no restoration and therefore in a permanent impact on the AONB; and might lead to expansion or intensification of site operations over time, which in turn has potential to substantially adversely affect landscape and visual character of the AONB.

Compliance with Policy C10 - Highways Officer Assessment

No highway issues raised.

Conclusion

An extant, temporary consent for waste uses is in place for part of the site, with site restoration required by 2022.

Given the site’s location within the AONB, the permanent retention of strategic waste uses on this site will not secure the site’s restoration and may result in a permanent impact on the AONB. Such an allocation may also might lead to intensification of the waste management use over time, which in turn has the potential to adversely affect landscape and visual character of the AONB.

RECOMMENDATION

It is not recommended that the site is allocated in the Site’s Local Plan because of the potential impact on the North Wessex Downs AONB should the operations continue on a permanent basis.

Site 003: Dix Pit, Stanton Harcourt

Site Information (as nominated in 2018) Site Location Dix Pit (Area 2), Stanton Harcourt Grid Reference SP408044

Administrative Area West Oxfordshire

Parish Stanton Harcourt

Site Nominee(s) FCC Environment

Proposed Change existing landfill from Development non-hazardous to inert waste. Permanent retention of existing recycling centre and waste transfer station for household/commercial and industrial waste

Site Area 0.66 ha

Existing Capacity 1 million cu,m landfill void 100,000 tpa (HWRC & WTS) Annual Throughput Unknown

Existing land use Existing non-hazardous waste landfill permitted to 31.12.2028 Existing Household Waste Recycling Centre and Waste Transfer Station with time limited permissions to

31.12.2028 (HWRC) and 31.03.2029 (WTS)

Access Existing access (within 1.6km of B4449)

Current levels and types of Unknown traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste • The site lies within 15km of Oxford. Strategy (Policy W4 and • Site lies over 3km from access onto the Oxfordshire Lorry Network (B4449). Policy W6) • Site does not lie within AONB. • The site does not lie within 200m of a SAC. • The site has a history of waste management use with existing access arrangements. District Local Plan Allocation • Site does not conflict with a District Local Plan Allocation. Biodiversity and Geodiversity • Site lies adjacent to a proposed local wildlife site - Dix Pit proposed Wildlife Site Extension. (Policy C7) • Site partially within a local geological site (Devils Quoits) – impacts would need to be avoided. • Site lies within 1km of SSSI (Stanton Harcourt). • Site lies in excess of 5km from International/European designated sites. Landscape / Visual (Policy • Site not within close proximity of an AONB. C8) Water Environment and • Site does not lie within a flood zone or source protection zone. Flooding (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site does not lie within an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 4 agricultural land. Historic Environment (Policy • Site partially lies within an area designated as a Scheduled Ancient Monument (Devils Quoits). C9) Transport and Access (Policy • No bus stops within 500m. C10) • No AM peak or PM peak traffic congestion areas identified within proximity to site.

• Site does not lie close to areas with history of RTIs. • Site lies over 3km from access onto the Oxfordshire Lorry Network (B4449). Public Rights of Way (Policy • No public right of ways within the site. A footpath passes close by to waste site and there may C11) be informal enjoyment of the water bodies. • A bridleway and footpath pass close to conveyor route and HWRC. • The current restoration plan includes reinstatement of a diverted footpath across the main landfill area. There was an application proposing to change this so it would skirt the edge instead but this application has still not been determined, primarily because of the need to resolve rights of way issues with the landowner. • There are also some permissive paths including an existing route providing access to the Devil’s Quoits and proposed new routes linked to a 20 year management plan.

Health and Amenity (Policy • Nearest residential dwelling lies approx. 90m to the south-east. C5) • Residential dwellings lie approx. 75m to the north-east. Green Belt (Policy C12) • Site lies outside of the Green Belt. Aerodrome Safeguarding • Site lies within London Oxford Airport, RAF Brize Norton and Dalton Barracks safeguarding (Policy M10) areas.

Cumulative Impact (minerals • Site within 3km of four existing waste sites: Lakeside Industrial Park, Rear of Cemex Batching Plant, Gill Mill Quarry and waste sites) and Sheehan Recycled Aggregates. • Site within 3km of an existing mineral site: Stanton Harcourt Quarry (Stonehenge Farm). • Site within 3km of two nominated waste sites: 103 Lakeside Industrial Estate and 236 Sheehan Recycled Aggregates. • Site within 3km of eight nominated mineral sites: SG-14 Stonehenge Farm, SG-18 Land near Standlake, SG-27 Vicarage Pit, SG-28 Guy Lakes North, SG-29 Sutton Farm, SG-30 Home Farm, SG-31 Land east of Sutton and SG-36 Land at Friars Farm.

Conclusion

The site comprises both inert landfill operations and a HWRC and Transfer Station. Key constraints relevant to site include its proximity to a scheduled ancient monument and access onto the Oxfordshire Lorry Route Network (B4449). Potential cumulative impacts would need to be considered further.

However, due to its proximity to Oxford and strategic potential to accept inert waste arisings at the latter end of the plan-period in accordance with Policy W4 the site is considered to be conform with the Waste Planning strategy with potential to provide capacity further within the plan-period beyond December 2028.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No:003 Site Name: Dix Pit, Stanton Harcourt

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview The Site benefits from historic consents for mineral extraction and backfilling.

The 2009 permission (09/118/2/P/CM) governs operations at the site and permits waste disposal operations until 31st December 2028. The permission permits the disposal of non-hazardous waste; however, the Site’s Environmental Permit has been varied to allow the filling of void with inert waste material.

The WTS and HWRC benefit from extant planning permissions until 2028 and 2029 respectively

No more than 100,000tpa is currently permitted to be imported to the WTS and Landfill.

• Landfill is permitted until 2028 with restoration by 2030 though the most recent application (MW.0088/16) wishes to bring the closure date forward. This would see the landfill close by 2021. • WTS is consented to operate until 31st March 2029. • HWRC is consented to operate until 31st December 2028 (planning permission 04/1486/P/CM) as amended by MW.0062/17.

ASSESSMENT

Compliance with Policy W5

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known irreplaceable habitats within or adjacent to the site. There are ponds within or adjacent to the site and records exist for several European Protected Species including Great Crested Newt and Water Vole. Records also exist for several notable and protected species including Smooth Newt, Grass Snake and numerous birds.

The site is within the Impact Risk Zones for Stanton Harcourt SSSI designated for its geological interest.

The site is adjacent to Dix Pit Local Wildlife Site (LWS) and its proposed extension and within the Lower Windrush Valley Conservation Target Area (CTA). There are current proposals for habitat enhancement and limited low-key public access. There is potential to support the aims and delivery of the Lower Windrush Valley Project.

The site is in existing waste management use and no additional ecological impacts are anticipated.

Compliance with Policy C8: Landscape – Landscape Officer Assessment

Development forms part of an existing complex of former and current mineral extraction and waste processing activities and the area has therefore been heavily modified. No additional impacts on local landscape character or nearby settlements are likely should operations on the site continue on a permanent basis.

There are currently no known historic landscape constraints and no impact on historic character expected.

The site would be visible in selected views from footpaths and recreational facilities (e.g. adjacent sports fields) but viewed in context of wider operations. Overall the landscape and visual impact of the proposal is considered to be low due to the use of the site, its context of mineral workings and landfill, and the limited visibility in public views.

The site is adjacent to and partially with the Devil’s Quoit scheduled monument. The monument has however been excavated and reconstructed and activities have been ongoing for a considerable period.

Compliance with Policy C10 - Highways Officer Assessment

HGVs will be routed from Dix Pit to the B4449 (Freight Priority Network - Tertiary) at Stanton Harcourt and would then travel 7.3km to A40.

There have been problems with HGVs through Sutton village and therefore a routing agreement would be required for any intensification of use.

Conclusion

Extant temporary consents exist on the site for waste management uses until 31st December 2028 (landfill and HWRC) and March 2029 for the WTS. Restoration of the landfill is required by 2030, although it is noted that there is currently an application before the Council that would see the landfill close by 2021.

There are no in principle reasons for preventing future waste management uses on the site that could not be overcome with appropriate mitigation, however intensification of the waste management use would not be appropriate for highway reasons.

RECOMMENDATION

As the site has planning permission until 2029, and given that Core Strategy Policy W11 already safeguards such operational waste management sites, allocation of the site in the Local Plan is not going to make a significant contribution to meeting waste management needs, particularly as intensification of any waste use would not be appropriate for highway reasons. It is not therefore recommended that the site is allocated in the Local Plan.

Site 008: New Wintles Farm, Eynsham

Site Information (as nominated in 2018) Site Location New Wintles Farm, Eynsham

Grid Reference SP 430111

Administrative Area West Oxfordshire

Parish Eynsham

Site Nominee(s) David Einig Contracting Ltd

Proposed Extension to existing Development aggregate recycling facility and increased throughput to 200,000tpa Site Area 5.26 ha

Existing capacity 170,000tpa

Annual Throughput 120,000 tpa (2017) 120,000 tpa (2016) 120,000 tpa (2015) Existing Land Use Existing permanent aggregate recycling facility Access Existing access onto Lower Road (within 850m of A40) Current levels and 88 HGV movements (44 in types of traffic and 44 out) (daily) movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site operates as an existing aggregate recycling facility with permitted capacity to (Policy W4) processes up to 170,000tpa, the site is therefore currently considered to be a strategic waste management facility in accordance with Policy W4. • The site lies within 15km of Oxford. • Site lies 0.6km from access onto the Oxfordshire Lorry Route Network (A40) to the south. • Site does not lie within 200m of SAC. • Site does not within, or in close proximity to AONB. District Local Plan Allocation • It should also be noted that the site lies within an area identified as part of the Oxfordshire Cotswolds Garden Village within the West Oxfordshire Local Plan 2031 • WODC also advise work has started on an Area Action Plan for the Garden Village and the site promoter is preparing an outline planning application. WODC also have significant concerns regarding the potential increase in tonnage and site size which would likely impact on the land-use distribution/budget of the garden village itself. • Eynsham Parish Council advise it seems more appropriate for an alternative site to be sought at this time so that operations can be transferred there before any new houses encroach on the recycling facility. Biodiversity and Geodiversity (Policy • Site located in excess of 5km from International / European designated sites. C7) • Site not within or adjacent to ancient woodland. • Site does not lie within 1km from SSSI, NNR and protected species. • Site does not lie within 500m of a SINC / local wildlife site or LNR. Landscape / Visual (Policy C8) • Site does not lie within, or in close proximity to AONB. Water Environment and Flooding • Site does not lie within a flood zone 2 or 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. Air Quality (Policy C5) • Site does not lie within or in close proximity to AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There are a cluster of listed buildings adjacent to the north of the site at City Farm as confirmed by WODC. • WODC advise there are significant concerns regarding the potential increase in tonnage and site size which would bring operations very close to the existing properties at City Farm, several of which are listed. • No known historic landscape or archaeological constraints.

Transport and Access (Policy • Site lies 0.6km from access onto A40. C10) • Poor access to public transport connections. • No AM peak or PM peak traffic congestion identified within close proximity to site. • Site lies within 3km of an area with history of serious to fatal RTI’s. • Site currently operating as a waste site, no access works required. Public Rights of Way (Policy C11) • Public right of way run along the southern, eastern and northern periphery of the site, as well as crossing the access to the site. Health and Amenity (Policy C5) • Site is adjacent to a residential property on the northern boundary. • And lies within 250m to another residential property to the south east. Green Belt (Policy C12) • Site does not lie in the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of one existing waste site: Worton Farm. waste sites) • Site lies within 3km of an existing minerals site: Cassington Quarry. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of four nominated minerals sites: SG-08 Lower Road, Church Hanborough, SG-20 Land between Eynsham & Cassington, SG-20a Wharf Farm and SG-20b Land at Eynsham.

Conclusion

The site currently operates as a permanent aggregate recycling facility with a permitted throughput of 170,000tpa.

It is situated in a fairly isolated location away from a large number of residential receptors, although a dwelling is located adjacent to the site’s northern boundary, and a further dwelling lies within 250m to the south east.

The site lies within 1km of access onto the Oxfordshire Lorry Route Network (A40), via Lower Road – a single carriage where a national speed limit restriction applies. This route also lies adjacent to one of the two existing dwelling which lie in close proximity to the site. The site currently generates up to 88 vehicle movements per day.

The site lies within 15km of Oxford and is therefore considered potentially suitable for small-scale, non-strategic and strategic waste activities in terms of its scale and proximity in accordance with Policy W4. Potential cumulative impacts will need to be considered further.

It should be noted that the site is included within an area that has been identified as a Strategic Location for Growth in the West Oxfordshire Local Plan 2031 - namely the ‘Oxfordshire Cotswolds Garden Village’.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 008 Site Name: New Wintles Farm, Eynsham

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview Existing site has permanent permission for an aggregates recycling facility with a capacity of 170,000tpa (permitted via a s73 application to increase throughput from 120,000tpa to 170,000tpa in March 2017 application reference MW.002/17).

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no records of irreplaceable habitats, notable habitats or European protected species within or adjacent to the site. Records exist for several notable and protected species including Barn Owl, Corn Mint, Brown Hare, Badger and numerous birds.

The closest Local Wildlife Sites are City Farm (and its proposed extension) and South Freeland Meadows.

A Biodiversity Management and Enhancement Strategy for the existing site area has been approved to increase biodiversity within the site and therefore any future development should not impact upon the restored habitat.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. The landscape context is of agricultural fields with mature hedgerows and trees.

The site proposed for extension reflects characteristic agricultural use of local landscape character. The extension and increase in vehicle movements are expected to adversely affect the local landscape character.

Development will affect views from Public Rights of Way and nearby residential views to the north; planting and bunding would be required to mitigate impact. The number of residential receptors will increase significantly with the proposed Garden Village development.

Compliance with Policy C10 - Highways Officer Assessment

The site is accessed off Lower Road and just 1km from the A40 (Freight Priority Network – Primary). The access road does not pass through any village. There is potential to improve/widen Lower Road.

Conclusion

Part of the site is currently in use as an aggregate recycling facility. Expansion of the site may compromise the future development of the proposed Oxfordshire Cotswolds Garden Village identified in the adopted West Oxfordshire Local Plan.

RECOMMENDATION

Expansion of the site may compromise the future development of the proposed Oxfordshire Cotswolds Garden Village identified in the adopted West Oxfordshire Local Plan and therefore it is not recommended that the site is allocated for expansion in the Local Plan.

Site 009: Worton Farm, Yarnton Site Information (as nominated in 2018)

Site Location Worton Farm, Yarnton

Grid Reference SP 474112

Administrative Area West Oxfordshire Parish Yarnton

Site Nominee(s) M&M Skip Hire Ltd T/A M&M Waste Solutions Proposed Recycling and recovery for non- Development hazardous + construction, demolition & excavation waste Site Area 3 ha.

Existing Capacity 75,000 tpa

Annual Throughput 73,900 tpa (2017) 74,900 tpa (2016) 67,500 tpa (2015) Existing Land Use Existing permanent skip waste recycling facility for non-hazardous + construction, demolition & excavation waste.

Access Existing access onto A40

Current Levels and 220 HGVs (skip lorries and Types of Traffic containers) (daily) Movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site is proposed as extension to the existing permitted site for materials processing, waste (Policy W4) segregation, bulking and transfer of non hazardous waste. The site has been used for unauthorised lorry parking and skip storage outside the site currently permitted for waste extraction, which is considered to be a strategic waste site in accordance with Policy W4. • The site lies within 15km Oxford. • The site is also within 1 km of access of the Oxfordshire Lorry Route Network (A40). • The site is not within 200m of a SAC. • The site does not lie within an AONB. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site lies approximately 500m to the north of the Pixey and Yarnton Meads SSSI. (Policy C7) • Site lies approximately 500m to the north of an International / European designated site (Oxford Meadows SAC). • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from NNR. • Site located within 1.5km to the northwest of a SINC. Landscape / Visual (Policy C8) • Site does not lie within AONB or close proximity to one. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site does not lie within AQMA. Soil Resources (Policy C6) • Site within an area of Grade 2 agricultural land but part of the been worked for minerals. Historic Environment (Policy C9) • Site in close proximity to Yarnton Manor (Grade II* Listed Building) and the associated Parkland (Grade II Listed Park and Garden) (within 500m to the north of the railway line). • A Scheduled Monument lies approximately 2km southeast of the site. • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies approximately 4.4km northwest of the site. • No known archaeological constraints. Transport and Access (Policy • The access road to the site is accessed directly from the A40, this is a private, gated haul road C10) which directly services the site. • Poor access to public transport connections. • Site lies within 3km of an area with a history of RTI’s. Public Rights of Way (Policy C11) • Site lies adjacent to a public right of way. Health and Amenity (Policy C5) • Site lies within 500m of residential properties (Church Lane to the north of the site).

Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within London Oxford Airport and Dalton Barracks safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of one existing waste site: Charlett Tyre Yard. waste sites) • Site lies within 3km of an existing minerals site: Cassington Quarry. • Site lies within 3km of one nominated waste site: 261 The Marshes. • Site lies within 3km of six nominated minerals sites: SG-04 Land at Mead Farm, SG-05 Land to the East of Cassington Quarry, SG-08 Land at Lower Road, Church Hanborough, SG-16 Land at Stonehouse Farm, SG-20 Land between Eynsham & Cassington and SG-20a Wharf Farm.

Conclusion

The site nominated is an extension to an existing recycling and recovery waste for non-hazardous and construction, demolition & excavation waste. The site currently has a capacity of 75,000 tpa.

Due to its operational capacity level, the site is considered a strategic waste site and lies within 15km of Oxford and also within 1 km of access of the Oxfordshire Lorry Route Network (A40). The site is therefore considered suitable in terms of its scale and proximity to this urban area in accordance with Policy W4.

The main constraint is that the site lies within the Green Belt. Development within the Green Belt would be inappropriate unless it would involve the replacement of a building, providing the new building is in the same use and not material larger than the one it replaces; or would comprise the partial or complete redevelopment of previously developed land which would have no greater impact on the openness of the Green Belt (NPPF 145).

It is considered that the site may have potential for waste management use and should be subject to detailed assessment. Potential cumulative impacts will need to be considered further.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 009 Site Name: Worton Farm, Yarnton

Stage 1b: Detailed Assessment

PLANNING HISTORY

A S.73 Application MW.0158/15 at the Cassington Quarry Plant site was permitted on 16.01.2016 for continued mineral working and restoration with imported materials, to enable working of minerals from beneath plant site. Mineral working is required to be completed by 31.12.2020 and the site restored by 31.12.2022. The nominated site is within the Cassington Quarrry permission area and part of the area of the plant site that is permitted to be extracted overlaps with the nominated site area.

The site has been used for unauthorised lorry parking and skip storage in association with Cassington Quarry Plant site.

An existing M&M skip hire and recycling site lies immediately to the north west of the nominated site. The substantive permission for this operation is MW.0108/09 dated 29.12.2009. This replaced earlier temporary permissions and allowed redevelopment of the facility. There is no limitation on throughput.

M&M have recently obtained permission on appeal for the permanent use of an adjacent site for skip storage (application MW.0090/17; appeal decision no. APP/U3100/W/18/3203111 dated 20.06.2019). A condition prohibits use of the site for any other purpose.

AD Plant (Severn Trent Green Power) The AD plant operated by Severn Trent Green Power (SGTP) adjoins nominated site C to the south west. This was originally permitted on 19.10.2009 – MW.013/08. It has permanent permission. The most recent amending permission – MW.0102/17 dated 08.03.2018 – allows an increase in the throughput of organic waste to 48,500 tpa.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The adjacent site is already in waste management use.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known records of irreplaceable or notable habitats within or adjacent to the site or records of European protected species. Records exist for other protected or notable species including numerous bird species (including barn owl), Grass Snake, Otter and Water Vole.

All or part of 5 SSSIs are within 2km of the site.

The site is adjacent to Cassington to Yarnton Gravel Pits Local Wildlife Site (LWS) and proposed extension and to the Oxford Meadows to Farmoor Conservation Target Area.

The overall impact is considered likely to be low, with the adjacent sites already in use. Significant additional ecological impacts within the existing working area are considered low providing no works proposed impact the adjacent LWS.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is within an area that is already heavily used and modified by gravel extraction and waste processing, and which defines the local landscape character.

A PRoW runs along the eastern boundary and parts of the northern boundary with views into the site. It is not however visible from many other public vantage points. No increased visual impact expected.

As an already disturbed site, no impact on historic landscape character is expected and there are no known historic landscape constraints.

Overall the use of the site for waste management purposes is not expected to have additional impacts on local landscape character and views.

Compliance with Policy C10 - Highways Officer Assessment

No highway issues raised. The site has good existing access direct on to A40.

Conclusion

The site is proposed to extend the operation of a Waste Transfer Station and MRF, a strategic waste site. The site is currently being worked for minerals with restoration consented by 2022.

The site is however in the Green Belt. Paragraph 144 of the NPPF advises that substantial weight should be given to any harm to the Green Belt. ‘Very special circumstances’ will not exist unless the potential harm to the Green Belt by reason of inappropriateness, and any other harm resulting from the proposal, is clearly outweighed by other considerations (Policy C12 of the Core Strategy). The land is not considered to be previously developed having regard to the definition of previously developed land set out in NPPF which states that land that has been developed for minerals extraction is excluded

from the definition where provision has been made for restoration. It is anticipated that the site will be restored under the extant consent (MW.0158/15) by 2022.

This site would therefore be inappropriate development in the Green Belt and should not be allocated unless there are exceptional circumstances to justify its release.

RECOMMENDATION

The site should not be allocated as it is inappropriate development within the Green Belt.

Site 010 – Sutton Courtenay Landfill (Areas 2 & 3), Appleford Sidings

Site Information (as nominated in 2018) Site Location Sutton Courtenay Landfill (Areas 2 and 3), Appleford Sidings Grid Reference SU516929

Administrative Area Vale of White Horse

Parish Sutton Courtenay

Site Nominee(s) FCC Environment

Proposed WTS/HWRC/hazardous Development waste treatment/waste wood treatment 50,00tpa (area 2); and Waste treatment/biomass treatment/waste to energy 200000tpa (area 3); for household, commercial and industrial, wood and hazardous waste

Site Area 14.2 ha Existing capacity 600,000 tpa landfill – (areas 4A, 4B and 4C 180,000 tpa - Composting and MRF 60000tpa WTS (area 1)

Annual Throughput Unknown

Existing land use Adjacent to existing landfill

site with end date 31.12.2030. Existing composting, MRF and WTS permitted to 31.12.2030. MRF currently mothballed and building used for waste transfer only. Access Existing access to A4130 Access to B4016 is restricted

Current levels and Unknown types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is an existing waste site with a permission to import up to 240.000tpaon a time limited (Policy W4) basis until 2030. • The site lies within 5km of Didcot and Abingdon and 15km of Oxford. • The site lies approximately 1km to the north of the existing Oxfordshire Lorry Network (A4130), via a direct access road. • Site does not lie within 200m of SAC. • Site does not lie within AONB. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located approximately 4.5km from Litte Wittenham SAC (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies within 3km, but in excess of 1km, of the North Wessex Downs AONB to the east of the site.

Water Environment and Flooding • The northern area (areas 4B & 4C) falls within flood zone 2, however areas 1, 2 and 3 are not (Policy C3 and Policy C4)) within flood zone 2 or a source protection zone. Air Quality (Policy C5) • Site is located over 3.5km from the closest AQMA (Abingdon). • Natural England advise the site will require further assessment in terms of air pollution effects on Little Wittenham and Cothill Fen SACs. Soil Resources (Policy C6) • Site is within an area of Grade 2 agricultural land, although is an existing developed site. Historic Environment (Policy C9) • There are listed buildings within 1km of site area 4B to the west at Sutton Courtney and area 2 to the northeast at Appleford. • There are no known historic landscape constraints and no impact on historic character is expected. Transport and Access (Policy • Site lies within 3km of area with history RTI’s C10) • The site lies approximately 1km to the north of the existing Oxfordshire Lorry Network (A4130), via a direct access road. Public Rights of Way (Policy C11) • A series of public rights of way run adjacent to the site’s boundaries. Health and Amenity (Policy C5) • There are a number of properties located within 1km of area 3 including Hill Farm to the southeast and Appleford to the east. Green Belt (Policy C12) • The site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site is located within the Dalton Barracks and RAF Benson aerodrome safeguarding areas. M10)

Cumulative Impact (minerals and • Site lies within 3km of seven existing waste sites: Didcot Strategic STW, Drayton Depot Transfer Station, Drayton waste sites) HWRC, Hill Farm, Milton Park, Sutton Wick Lane and Culham JET. • Site lies within 3km of two existing minerals sites: Sutton Wick Quarry and Sutton Courtenay Quarry (Bridge Farm). • Site lies within 3km of three nominated waste sites: 217 Culham No.4 Site, 234 Didcot STW and 276 Oday Hill. • Site lies within 3km of three nominated minerals sites: SG-17 Land at Culham, SG-62 Appleford and SG-67 Sutton Wick Quarry.

Conclusion

The site currently comprises a number of waste management processes including composting, waste transfer. material recovery and landfilling activities. It is therefore suitable in terms of its scale and proximity to these areas to provide small-scale, non-strategic and strategic waste management provision in accordance with Policy W4.

The site lies approximately 1km to the north of the existing Oxfordshire Lorry Network (A4130) via a direct access road which runs adjacent to 3 residential properties.

Due to the limited constraints affecting the nominated sites and the site’s proximity to major urban areas in accordance with Policy W4, there is potential for these areas to provide further waste management capacity in terms of both intensification and diversification. However, HV cables which run across the site (as confirmed by National Grid) will need to be considered further when assessing the sites level of suitability as would the potential impact on air pollution and effects on Little Wittenham and Cothill Fen SACs (as confirmed by Natural England). Potential cumulative impacts will need to be considered further.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 010 Site Name: Sutton Courtenay Landfill (Areas 2 & 3) Appleford Sidings

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

Area 1 & Area 2 Area 1 is an existing MRF, WTS and Green Waste Composting Facility, with two currently active planning permissions: MW.0090/13: permitted on appeal 17.06.2014 (APP/U3100/A/13/2210015): to continue the establishment of recycling facilities without complying with conditions (this covers the MRF and green waste composting facility): MW.0088/13: permitted on appeal 17.06.2014 (APP/U3100/A/13/2210018): construction of a waste transfer facility to handle 60,000tpa of non-hazardous waste and 200tpa of clinical waste. Both permissions have a condition requiring the operations to cease and buildings, plant and machinery to be removed and restoration completed by 31.12.2030. Area 2 is within the red line area for permissions MW.0090/13 and MW.0088/13.

Area 2 is located to the north of the existing MRF and WTS building and is proposed for new built waste management uses (WTS / HWRC / hazardous waste treatment / waste wood treatment). The site may either be accessed through the existing MRF/ WTS facility or from a new access road to the east from Corridor Road. To the south is the existing MRF/ WTS, to the west the green waste open windrow composting facility and to the north is the aggregate extraction / processing plant area. To the east, beyond Corridor Road, is an Asphalt Production Facility, operated by Hanson and the Appleford Sidings aggregates and waste railhead. The site is located centrally within the Sutton Courtenay Waste Management Complex.

Area 3 The site is mostly previously quarried, landfilled and restored land; it includes areas to the east and west of Hobby Horse Lane South and is proposed for new built waste management uses (waste treatment / biomass treatment / waste to energy). The western area is located to the south of the existing green waste open windrow composting facility and MRF/ WTS. The area to the east is located to the south of the asphalt production plant and Appleford Sidings aggregates and waste railhead and to the north of the existing landfill. This site is partly occupied by an existing landfill gas utilisation plant, permitted by: MW.0156/10; permitted 27.01.2011: to regularise the layout of the existing landfill gas utilisation compound and install one additional engine and associated plant and equipment. Condition requires removal of plant within 6 months of cessation of electricity generation from landfill gas and restoration

within a further 12 months. The site is located centrally within the Sutton Courtenay Waste Management complex.

Area 4A This is the current landfill area. Area 4B This site is also permitted to receive waste. Area 4C This is an existing mineral extraction / processing plant area with permission for backfill These areas are all covered by permission MW.0039/15 (the currently active planning permission): MW.0039/15; permitted 03.08.2015: to continue the development of permitted by P14/V0479/CM (for the deposit of non-hazardous waste including surcharging the existing landfill, extending the duration of landfill and clay extraction operations, temporary storage of PFA and ancillary activities to restoration) without complying with conditions 1, 10, 15, 17, 28, 30, 32 and 34, to amend the landfill phasing, restoration plan for phase 3, restored contours of phase 3 and the restoration method for phases 3 and 4 at Sutton Courtenay Landfill Site. (This permission covers a wider site at Sutton Courtenay than just site 4A.) Conditions on this permission require: Cessation of extraction of sand or gravel by 31.12.2020 or by two years from the final restoration of Bridge Farm Quarry; No extraction of clay after 31.12.2020 except clay required for landfill engineering works; No deposit of waste after 31.12.2030; All plant, buildings, machinery and structures to be removed and the land restored by 30.09.2036 (except plant or facilities for the monitoring or control of landfill gas or leachate and the access roads shown in brown and the land shown as “area of industrial development ‘coffin area’’' and ‘rail sidings/plant site’ on approved plan SC 2/2 – these have permanent permission); No more than 600,000 tonnes of waste shall be delivered to the site in any calendar year, of which not more than 350,000 tonnes shall be delivered by road.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

Area 3 is largely undeveloped land which is partly developed for ancillary waste uses (landfill gas management). Area 2 is also undeveloped land which lies adjacent to existing waste uses.

The supporting text to Policy W4 acknowledges that extensions to existing [waste] sites may offer a better option than development of a new [waste] facility elsewhere. The supporting text also acknowledges the benefits, through operating synergies and reduced waste movements, of co-locating waste management uses. Future waste proposals at Sites 2 and 3 are deemed to have potential to demonstrate the most suitable and sustainable option in accordance with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known irreplaceable habitats within or adjacent to the site and the only notable habitats within the site are the waterbodies from existing

extraction permissions.

There are records for numerous bird species including Barn Owl and Red Kite. Other notable species include Otter, Smooth Newt and Water Vole.

The site is subject to high levels of existing disturbance under existing permissions. No significant additional ecological impacts are anticipated, beyond those currently mitigated against.

Compliance with Policy C8: Landscape – Landscape Officer Assessment

The site is not within a designated landscape but approximately 1km form the North Wessex Downs AONB and likely to be visible in distant views from the AONB but viewed in the context of other development including Didcot Power Station and existing landfill.

Impact on local landscape character expected to be limited due to location and context of similar uses in vicinity. Increased vehicle movements have potential to impact on local landscape character.

The proposed development comprises an intensification of existing uses. Restoration of landfill has potential to deliver landscape benefits in the long term and should not be compromised by allocations.

Compliance with Policy C10 - Highways Officer Assessment

There is the potential for rail transport at this site.

The existing access onto the A4130 is suitable for HGV movements with the minimal amount of engineering/mitigation.

The access onto the A4130 is now also required for the allocated Enterprise Zone (D-Tech). Any increase in HGVs from this site would put pressure on the Manor Bridge roundabouts and therefore they require the Science Bridge and A4130 widening schemes as a minimum.

At peak times, queuing of traffic along key routes in the Didcot area cause the blocking of junctions on the highway network, resulting in a situation akin to gridlock, with queues slow to disperse and highway users performing ‘unorthodox’ manoeuvres and blocking straight ahead travel. Any new trips will add to the delay experienced along these highway corridors and would increase the periods of blocking of junctions and carriageways.

Oxfordshire Local Transport Plan includes a new Science Bridge crossing and widening of the A4130 in Didcot which will relieve pressure on this part of the network; however, until such an improvement is realised, the LHA is having to assess all development proposals on their merits, to protect against any development in Didcot that would add new peak hour trips to an extremely sensitive part of the network, without appropriate mitigation.

Conclusion

Areas 2 and 3 are located centrally in the waste management complex and as such the principle of waste uses is acceptable. However, given the potential for any new development to compound current highway issues, allocation of these sites would be dependent on appropriate highways mitigation or the completion of the schemes proposed in the Oxfordshire Local Transport Plan.

RECOMMENDATION

It is recommended that the site is allocated in the Local Plan for waste management uses.

Site 011: Finmere Quarry, Banbury Road, Finmere Site Information (as nominated in 2018)

Site Location Finmere Quarry, Banbury Road, Finmere Grid Reference SP627323 Administrative Area Cherwell Parish Finmere

Site Nominee(s) AT Contracting & Plant Hire Limited Proposed Landfill extension, retention of Development MRF, secondary aggregate recycling and waste treatment facility (EfW) for non-hazardous C&I wastes, total 150,000tpa Site Area 9.6 ha

Existing capacity Unknown Annual Throughput Unknown

Existing land use Landfill (permitted to 2028) and MRF (permitted to 2020) Planning application in for these areas. MW.0029/19.

Access Existing access from the A421 (Banbury Road) Current levels and Average number of HGV types of traffic movements per working day for: Landfilling of non-hazardous movement waste: 35.5 Landfilling of inert waste: 22.5 Secondary Aggregate Recovery: 15

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4 and W6) • The site has direct access onto the A421 which is part of the Oxfordshire lorry route network. • The site is not located within the AONB • The site is not within a 200m buffer of a Special Area of Conservation. • As an existing landfill site Policy W6 also applies. • The Core Strategy identifies the site as a strategic landfill site on the Waste Key Diagram with a permitted end date of 2028 (Table 11 OMWLP Core Strategy) District Local Plan Allocation • The site is not allocated in the District Local Plan. • District Council has no principle objections at this stage. Biodiversity and Geodiversity • Ancient woodland lies approx. 850m to the west of the site. (Policy C7) • SSSI (Tingewick Meadows) lies approx. 2km to the east of the site. Landscape / Visual (Policy C8) • Site does not lie within AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Site includes surface water bodies and lies close to a surface water body to the west of the site. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies within land designated as Grade 2 and 3 BMV agricultural land Historic Environment (Policy C9) • Nearest heritage receptor is Widmore Farmhouse, a Grade II listed building approx. 400m to the west. • Site is a former quarry and landfill and any archaeological features will have been removed. As such there are no archaeological constraints. • No impact on historic character expected Transport and Access (Policy • Nearest bus stops are in Finmere, approximately 1km to the north-east. C10) • Site lies in proximity to existing AM peak congestion areas on Featherbed Lane – A421 junction. • Site lies within 3km of area with history of serious RTI’s. Public Rights of Way (Policy C11) • A bridleway (213/7/20) intersects the site however this has been temporarily diverted until the 31/12/19 Health and Amenity (Policy C5) • Residential dwelling (Boundary Farm) within 350m to the east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area.

M10)

Cumulative Impact (minerals and • Site lies within 3km of an existing waste site (Finmere Quarry). waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of a nominated minerals site: SG-63 Finmere Quarry.

Conclusion

The site is identified as a strategic landfill site in the OMWLP Core Strategy with direct access onto the Oxfordshire lorry route network. There are no major constraints that could not be overcome with appropriate mitigation.

The site does not lie in within a suitable distance to any urban area identified within Policy W4, however, due to its strategic potential to continue to accept inert waste arisings beyond 2028, the site is considered to conform with the waste planning strategy set out in the Core Strategy and is therefore considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 011 Site Name: Finmere Quarry

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

There are four currently active planning permissions.

Non-Hazardous Landfill (Includes the areas nominated for Landfill Extension; Retention of MRF; Secondary aggregate recycling; and Waste Treatment Facility.) MW.0003/19, permitted 15.04.2019: Section 73 application to vary the pre and post settlement contours for cells 1, 3, 6, 7A, 7B and 9; to amend the deadlines for the completion of landfilling, capping and restoration of cells 1, 3, 6, 7A, 7B and 9; and to make minor revisions to the position of the internal boundaries between cells 10, 11 and 11A and to the landfill sequence. Conditions require: • Completion of deposit of waste by 06.01.2028; • Completion of restoration by 06.01.2032.

MRF (Site lies within non-hazardous landfill permission area.) MW.0139/15, permitted 29.01.2016: Section 73 application for planning permission to continue development without complying with Conditions 1, 7, 17 and 26 (to allow the storage of Refuse Derived Fuel (RDF) and Solid Recovered Fuel (SRF) outside the storage bay at the consented MRF (the subject of planning permission 10/00361/CM), to amend the operational hours of the MRF and to extend the acoustic barriers) of planning permission reference 15/00245/OCC. Conditions require: • Acceptance of waste shall cease by 31.12.2020; and all buildings, plant and machinery shall be removed and restoration be completed by 31.12.2021; • Annual throughput of waste shall not exceed 150,000 tpa.

Site Reception Compound (Site lies within the non-hazardous landfill permission area, within the area nominated for landfill extension.) MW.0060/17, permitted 02.11.2017: Replacement site reception compound and related facilities. Condition requires: • All buildings, structures and hardstandings to be removed and the site to be restored by 06.01.2032.

0 Sand & Gravel Extraction and Inert Landfill (South eastern mineral extraction area – adjoins area nominated for secondary aggregate recycling to the east) MW.0083/17, permitted 26.01.2018: Section 73 application to continue sand and gravel and clay extraction for use in on-site landfill engineering permitted by planning permission no. 10/01515/CM without complying with conditions B1, B2, B3, B8, B9, B14, B16, B17, B20, B26, B32, B35, B37 and B39 to enable the development (including restoration) to continue until 30th September 2031, alternative screening to be provided along the eastern boundary and the updating or deletion of conditions which no longer apply. Conditions require: • Cessation of mineral extraction by 06.01.2030; • Cessation of deposit of quarry reject material by 06.01.2031; • Completion of restoration 30.09.2031. • Excavated minerals shall not be transported onto the public highway and shall only be used in the area the subject of planning permission MW.0004/17 (superseded by MW.0139/15 – the non-hazardous landfill area).

There are seven current applications for the Finmere Quarry site that are yet to be determined:

• MW.0142/16 – Continuation of development without complying with conditions A1, A3, A22 and A33 of planning permission reference 10/01516/CM (MW.0142/10) to provide for an extension of the life of the development of the consented extension. (This relates to a permission MW.0142/10 granted 21.12.2010 for sand and gravel extraction from land to south west of Finmere Quarry and Landfill site, but with the processing plant located on the area now nominated for secondary aggregate recycling and using the existing quarry/landfill access. Permission MW.0142/10 has expired.)

• MW.0026/19 – Extension of area approved for clay extraction. (This is for land to the east of the existing permissions for non-hazardous landfill and mineral extraction; it would be a new extraction area.)

• MW.0027/19 – Extension to the area for non hazardous waste landfill. (This is for approximately the same area as the area nominated for landfill (non-hazardous waste) extension.)

• MW.0029/19 – Section 73 application to planning permission 15/02059/OCC (MW.0139/15) to allow for the operation of the Material Recovery Facility (MRF) until January 2028. (This is similar to the nomination for retention of the MRF.)

• MW.0030/19 – Extension to area approved for sand and gravel extraction and retention of processing and concrete batching plants. (This is for extraction of sand and gravel from land to the north of the existing quarry & landfill site, the same area as mineral site nomination SG- 63, but including retention of the processing etc plant in the area nominated for secondary aggregate recycling.)

• MW.0031/19 – Application for secondary aggregate recycling. (This is for the area nominated for secondary aggregate recycling.)

• MW.0041/19 – Continued use of a clean water lagoon and silt pond in phase 1 of the area approved for the extraction of sand and gravel and clay for the use in the landfill engineering under planning permission 17/02083/CM (MW.0083/17). (This relates to the south eastern mineral extraction area – see MW.0083/17 above.)

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site currently operates as an existing waste management facility and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment There are no irreplaceable habitats within or adjacent to the site. Notable Habitats within the site include Finmere Plantation woodland, bound by existing operations and ponds.

Records of European protected species within or adjacent to the site include Great Crested Newt (existing licence for translocation) and for several bat species.

Other protected or notable species include Badger, Smooth Newt, Grass Snake and numerous other notable species.

Overall the works are within existing areas of operations. Ecological surveys undertaken to data have confirmed the site provides opportunities for a number of protected species. Mitigation measures are expected to limit impacts on protected species, with no anticipated residual harm. Restoration proposals will likely improve biodiversity within the site

Compliance with Policy C8: Landscape – Landscape Officer Assessment

The site is not within a designated landscape or its setting.

The site forms part of Finmere Quarry and landfill that has been partly restored and therefore limited additional impact on local landscape character is expected.

Restoration offers opportunities for landscape enhancements in the long term.

There are several Public Rights of Way (PRoW) in the vicinity which offer occasional and/or glimpsed views of the site.

The site is generally quite well screened however a temporary impact is expected. There would be occasional and/or glimpsed views of the site from several PRoWs.

The landfill extension might result in a slight increased visual impact but restoration has potential to deliver landscape and visual benefits in the long term.

Overall impacts on landscape character and views are not expected to increase.

Compliance with Policy C10 - Highways Officer Assessment The site has access straight on to A421 (Freight Priority Network - Primary) without passing through any villages. No impact on the local lorry route is expected.

Existing access has good visibility, and gates set well back. There is a right turn filter lane from A421

Conclusion

The site is identified as a strategic landfill site in the OMWLP Core Strategy with direct access onto the Oxfordshire lorry route network. Restoration of the site has potential to deliver landscape and visual benefits in the long term as well as improvements to biodiversity.

RECOMMENDATION

It is recommended that the site is allocated in the Waste Local Plan for waste management uses.

Site 018: Holloway Farm, Milton Common, Wheatley

Site Information (as nominated in 2018) Site Location Holloway Farm, Milton Common, Wheatley

Grid Reference SP626045

Administrative Area South Oxfordshire

Parish Great Milton

Site Nominee(s) Sheehan Haulage and Plant Hire Ltd

Proposed Aggregate recycling for Development construction, demolition & excavation waste

Site Area 2.7 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Greenfield

Access Potential access onto Church Hill. Site adjacent to the A40/M40 junction.

Current levels and N/A types of traffic

movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site does not currently operate as a waste management facility. (Policy W4) • The site lies within 15km of Oxford. • The site has direct access to Church Hill which has good access to the Oxfordshire Lorry Route network (M40/A40). • The site is not located in an AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR.

Landscape / Visual (Policy C8) • Site not located within an AONB. Water Environment and Flooding • Site does not lie within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site does not lie within an AQMA. Soil Resources (Policy C6) • The site is within an area of Grade 3 BMV. Historic Environment (Policy C9) • The site lies within 500m of a listed building at Lower Farm. • The site has been extensively disturbed by previous development. No archaeological constraints. Transport and Access (Policy • Church Hill serves existing employment uses. C10) • There is a bus stop 500m from the site at the Wheatley service station. • PM peak congestion areas identified in close proximity to the site. • The site is located within close proximity to an area with a history of RTI’s. • Highways England advise that it would be concerned if any new direct accesses were proposed to the SRN without further consultation and if any site activities were in close proximity to the SRN boundary in terms of a potential impact of the integrity of Highways

England’s assets. Public Rights of Way (Policy C11) • No public rights of way in the vicinity of the site. Health and Amenity (Policy C5) • The site is opposite to a residential property to the north which operates as a B&B. Wheatley services, including a hotel is located at the A40/M40 junction to the north. Green Belt (Policy C12) • Site is within the Oxford Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Chalgrove aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of an existing waste site: Milton Pools Great Haseley. waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

This site is within the Oxford Green Belt. Waste uses are inappropriate development, and by definition harmful, to the Green Belt. Very special circumstances would need to be demonstrated for siting waste proposals in the Green Belt, including the need for the type of facility having regard to suitable alternatives.

This site lies within 15km of Oxford and, in accordance with Policy W4, is appropriately located to provide strategic, non-strategic and small-scale waste management capacity with good access to the Oxfordshire Lorry Network (A40/M40).

The site is a relatively thin strip of undeveloped land encircled by the A40 and its north/south junction with the M40 motorway, with some existing employment uses in the vicinity including the Ramada Oxford Service Station.

It is considered that the site should be taken forward for further detailed assessment having regard to NPPF that development must preserve the openness of the Green Belt and not conflict within the purposes of including land within (with reference to paragraph 134).

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No:018 Site Name: Holloway Farm, Milton Common

Stage 1b: Detailed Assessment

PLANNING HISTORY

No planning history

ASSESSMENT

Compliance with Policy W5

The site does not comprise previously developed land currently in waste management use and does not appear to contain any agricultural buildings. The site is also not allocated for employment use or identified in South Oxfordshire’s Employment Land Review (2015). Waste management proposals at this site would therefore need to demonstrate that they are the most suitable or sustainable option.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no records of any Irreplaceable Habitats within or adjacent to the site. Records of Notable Habitats include the presence of grassland habitats.

Records for several notable and protected species include Barn Owl, Brown Hare, Water Vole, Otter, Badger and numerous birds.

Overall the ecological impacts of the proposals are likely to be low.

Compliance with Policy C8: Landscape – Landscape Officer Assessment

Development is unlikely to impact on landscape character. There are no known historic landscape constraints.

The development is expected to have a low impact on local character and views despite this being a permanent use on a greenfield site because the site is located between major roads, service station and other adjacent industrial uses which reduce the landscape and visual sensitivity of the site.

Compliance with Policy C10 - Highways Officer Assessment

As there is no other means of access to this site, it is assumed that access would be via Church Hill and that the site nominator has a right of access over this road.

The dearth of HGV parking along this part of the A40/M40 corridor is a recognised issue and results in problems with overnight usage of laybys on the Oxford eastern bypass. Careful consideration will be required to ensure that HGVs would be able to stack within the site as necessary.

This site is located adjacent to the A40/London Road junction and the M40 junction 8A. These experience significant peak hour congestion and therefore controls over hours of working are likely to be required to avoid HGV traffic at peak hours exacerbating this. On this basis the site may be suitable for certain type of waste uses but waste uses that generate a significant amount of traffic may be unacceptable.

Conclusion

The site is located in the Green Belt. Paragraph 144 of the NPPF advises that substantial weight should be given to any harm to the Green Belt. ‘Very special circumstances’ will not exist unless the potential harm to the Green Belt by reason of inappropriateness, and any other harm resulting from the proposal, is clearly outweighed by other considerations (Policy C12 of the Core Strategy).

The site is located in an already heavily urbanised area, between the M40 and A40. It is considered therefore that the potential allocation of this site is unlikely to cause substantial harm to the openness of the Green Belt or to the five purposes of the Green Belt as set out paragraph 134 of the NPPF. Notwithstanding this, the allocation of this site should only be considered where the benefits of the proposal would clear outweigh other considerations, particularly in relation to highways. It is unlikely that it will be possible to demonstrate that there are no other more suitable and sustainable alternatives to meet the County’s waste management needs.

RECOMMENDATION

The site would be inappropriate development in the Green Belt and should not be allocated unless there are exceptional circumstances to justify its release.

Site 026 – Whitehill Quarry, Burford

Site Information (as nominated in 2018) Site Location Whitehill Quarry, Burford

Grid Reference SP 269 107

Administrative Area West Oxfordshire

Parish Shilton

Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Aggregates Recycling Facility Development for inert construction, demolition and excavation wastes to restore the quarry site. Site Area 15 ha

Existing Capacity n/a

Annual Throughput n/a

Existing land use Existing quarry

Access Existing access onto A40

Current Levels and n/a Types of Traffic Movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site appears to be an inactive quarry. (Policy W4 and W6) • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. • The site is located directly off the A40 and therefore has access to the Oxfordshire Lorry Route (A40). • The site is not within 200m of an SAC. • The site does not lie within an AONB. • The site is nominated for an aggregates recycling facility for inert construction, demolition and excavation wastes to restore the quarry site, this would not be in conflict with policy W6 providing there would be an overall environmental benefit. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site within the Whitehill Quarry Local Geological Site. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies adjacent to the Cotswolds AONB. • Natural England’s comments at the issues and options stage recommended that consideration will need to be given to inter -visibility between the following sites and AONBs; where this occurs Landscape and Visual Impact Assessment will need to be undertaken to inform consideration of these sites for inclusion in the plan. Water Environment and Flooding • Site does not lie within a flood zone or source protection zone. (Policy C3 and Policy C4)) • The Environment Agency’s comments at the issues and options stage identified that this site is located on a principal aquifer and there is a private water supply adjacent at Sturt Farm. This is a potential groundwater quality issue that might need to be risk assessed prior to the development. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There is a listed building 300m to the north east of the site off White Hill; a second 1km to the north at Widford; and a third 800m to the south east at Stonelands. • This area has been extensively disturbed by previous development. No archaeological constraints.

Transport and Access (Policy • Site lies adjacent to the A40. C10) • Poor public transport connections. • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies within area identified as having a history of fatal RTI’s. Public Rights of Way (Policy C11) • There is a public footpath which crosses the site east to west (149/19), which has been temporary diverted 03.03.23. • There is also a bridleway which runs adjacent to the eastern boundary of the site (Definitive Map of Public Right of Way for Oxfordshire, 2006). Health and Amenity (Policy C5) • There is a residential property in very close proximity (approximately 60m) from the site entrance. • There are other residential properties within 500m of the site. Green Belt (Policy C12) • The site is not located in the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of an existing waste site: Shipton Hill. waste sites) • Site lies within 3km of an existing minerals site: Burford Quarry. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of two nominated minerals sites: CR-07 Adjacent to Whitehill Quarry and CR-10 Burford Quarry SW extension.

Conclusion

The site is an inactive and dormant quarry. The site does not lie in close proximity to any urban area as identified within Policy W4. However, the site provides direct access onto the Oxfordshire Lorry Route Network (A40). The site may therefore be suitable for strategic, non-strategic or small-scale waste activities in accordance with Policy W4.

With regards to the sites potential to accept inert waste as infill, overall environmental benefit should be demonstrated to ensure conformance with Policy W6.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 026 Site Name: Whitehill Quarry, Burford

Stage 1b: Detailed Assessment

PLANNING HISTORY

The site has permission for quarrying under 3 determinations of new conditions under IDO and ROMP procedures approved 02.07.2004 – MW.006/04, MW.007/04, and MW.008/04. Mineral extraction is required to cease by 21.02.2042, with restoration of the site by 21.02.2043.

There is no permission for waste management at this site.

Planning consent allows for quarrying until 2042 and no requirement for this to be continuous. Site is currently inactive (2017 monitoring report). Final restoration scheme, including phasing, aftercare and a revised timetable for the drystone walling is outstanding.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is currently dormant but with an extant consent for mineral working therefore complies with Policy W5. However, the site also lies in close proximity to the Cotswolds AONB. Waste proposals at this site should therefore be considered against Policy C8.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no records of irreplaceable habitats or notable habitats within or adjacent to the site. Records exist for numerous bat species which are a European protected species. Records exist for several other protected or notable species including numerous bird species (including Barn Owl), Otter, Badger, Brown Hare and Water Vole and Corn Mint.

Conservation Target areas (CTAs) include the Upper Windrush CTA 350m to north and the South Cotswold Valleys CTA 900m to south

Overall impacts are likely to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment The site is adjacent to Cotswold AONB boundary (A40).

A bridleway runs along the eastern boundary of site, and a footpath crosses the site at northern end, both of which might offer views into the site. Development is however unlikely to be visible from other public rights of way in the AONB due to the rolling topography. There may be occasional glimpsed views from A40.

Any development at the site will be viewed in the context of the existing quarry and a previously disturbed site. There are currently no known historic landscape constraints.

Additional impacts on landscape character and views are not expected and it is anticipated that the proposed inert landfill will facilitate the site’s restoration in particular given the site’s location adjacent to the AONB.

Compliance with Policy C10: Transport - Highways Officer Assessment

It is not anticipated that there will be a significant impact on the local lorry route. Access to the site is straight on to A40 (Freight Priority Network - Primary) that bypasses local villages. No significant local traffic impact is anticipated, although the A361 roundabout (1 mile west of site) can be congested at times. The existing access to the quarry has good visibility with the access gates set well back and a right turn filter lane from A40.

Conclusion

The site provides direct access onto the Oxfordshire Lorry Route Network (A40) and may be suitable for strategic, non-strategic or small-scale waste activities in accordance with Policy W4. The Core Strategy Policy W6 states that priority will be given to the use of inert waste that cannot be recycled as infill materials to achieve the satisfactory restoration and after use of active or unrestored quarries.

Any waste development on the site should avoid sterilising any remaining mineral resource. This assessment would need to be considered at the planning application stage.

On this basis and having regard to the site’s current state as an unrestored mineral site adjacent to the Cotswold AONB, it is considered that the allocation of the site for infill with insert waste is likely to result in a positive environmental benefit through the restoration of the site to deliver landscape benefits and offering potential opportunities for beneficial after use.

RECOMMENDATION

The site is considered suitable for allocation.

Site 103: Land at Lakeside Industrial Estate, Standlake

Site Information (as nominated in 2009) Site Location Land at Lakeside Industrial Estate, Cotswold Drive, Standlake Grid Reference SP383044

Administrative Area West Oxfordshire

Parish Standlake

Site Nominee(s) Ethos Recycling Limited

Proposed Residual Waste Treatment Development Site Area 3.2 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Currently undeveloped with history of waste use. Access New bellmouth access directly off Cotswold Dene which in turn gives access directly onto the A415.

Current levels and N/A types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site lies within 15km of Oxford. (Policy W4) • Site is within 200m of the Oxfordshire Lorry Route (A415). • The site is not located in an AONB. • The site is not within a 200m of a Special Area of Conservation. District Local Plan Allocation • The site is not allocated in the District Local Plan. • West Oxfordshire District Council advises that the majority of the site is allocated in the adopted and emerging Local Plan for employment use (B2 – B8 and similar sui generis uses only). Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. • Natural England advises that the site would require further assessment to rule out potential indirect impacts or to inform mitigation in terms of air pollution effects on Oxford Meadows and Cothill Fen SACs Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • No impact on historic environment. • Site has been extensively disturbed by previous development as such there are no archaeological constraints. • OS map indicates Site of Settlement (Bronze Age to Anglo Saxon). • Historic sensitivity expected to be low due to more recent developments.

Transport and Access (Policy • The site has direct access to the A415 via the existing industrial estate. C10) • There are bus stops less than 200m from the site. • No AM peak or PM peak traffic congestion identified within proximity to site. • Brighthampton to the south of the site has a couple of serious RTI histories.

Public Rights of Way (Policy C11) • No public rights of way within the site. • There is a public right of way to the south with views of the site in the context of the industrial estate Health and Amenity (Policy C5) • The site lies is approximately 500m from the closest property in Brighthampton to the south. Green Belt (Policy C12) • Site is not located within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of five existing waste sites: Lakeside Industrial Park, Rear of Cemex Batching Plant Dix Pit waste sites) (Landfill, HWRC & Transfer Station), Gill Mill Quarry (Landfill & Recycling) and Dix Pit (Sheehan Recycling). • Site lies within 3km of an existing minerals site Gill Mill Quarry. • Site lies within 3km of two nominated waste sites: 003 Dix Pit and 236 Sheehan Recycled Aggregates. • Site lies within 3km of five nominated minerals sites, SG-18 Land near Standlake, SG-27 Vicarage Pit, Cogges Lane, SG-28 Guy Lakes North, adj B4449, SG-30 Home Farm, Brighthampton and SG-36 Land at Friars Farm.

Conclusion

The site is undeveloped and is located adjacent to southwest boundary of the Lakeside industrial estate. The site appears to have been previously in waste use with part of the site benefiting from a CLEUD for the processing of inert waste and another part with consent for open storage.

The site is suitably located to the strategic road network accessed through the industrial estate. The site also lies within 15km of Oxford and is therefore considered suitable to provide small-scale, non-strategic and strategic scale waste management activities in accordance with Policy W4.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 103 Site Name: Land at Lakeside Industrial Estate, Standlake

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

A small part of the site in the south west corner is authorised under a CLEUD for the storage of inert builders and contractors waste in one area and the siting of recycled material and other structures in another area (W96/1038 dated 08.01.1997).

In January 2019, previously deposited C&D waste was being removed from the site surface and stockpiled along the south-western boundary. Enforcement case was subsequently opened regarding stockpiling of material and unauthorised removal of waste. Case was closed in March 2019 as OCC considered it was not expedient to take action at the time.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

A small part of site benefits from a CLEUD for waste management uses and it can therefore be considered to be partly previously developed. The wider site adjoins the Lakeside Industrial Estate and is allocated in the adopted and emerging West Oxfordshire Local Plan for employment use (B2 – B8 and similar sui generis uses only). As such it would accord with Core Strategy Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no international designations, irreplaceable habitats or notable habitats within or adjacent to the site. Great Crested Newt, a European protected species has been recorded approximately 130m from site. Records for other protected / notable species include numerous bird species, including Barn Owl, Otter, Badger, Brown Hare and Water Vole

The Lower Windrush Valley Conservation Target Area lies approximately 525m to east/north.

There would be some potential loss of secondary vegetation with limited GI opportunity.

Overall impacts are likely to be low, given current habitats present.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. The landscape context is of an industrial estate on three sides and open countryside to the South. Noise and HGV movements associated with proposal might affect wider landscape character area.

The site is not considered to be sensitive in landscape and visual terms due to its location within an industrial estate. Overall the landscape and visual impact is considered to be low.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site has good existing access direct on to A415 that does not pass through any villages. HGV movements are through the industrial estate between the site and the A415. The A40 is 6.0km from the site.

Conclusion

Part of the site benefits from a CLEUD for waste management uses with the remainder of the site primarily allocated in the West Oxfordshire Local Plan for employment use (B2 – B8 and similar sui generis uses only).

The wider site is seen in the context of the adjoining industrial estate and therefore landscape impacts would be low. The site benefits from good access to the highway network and there are no in principle reasons why this site should not be allocated in the Local Plan for waste management uses.

RECOMMENDATION

The majority of the site is allocated in the adopted West Oxfordshire Local Plan for B2 – B8 or similar sui generis use with the remainder of the site benefitting from a CLEUD. A waste management use would not be inconsistent with this allocation and therefore it is recommended that the site is allocated in the Waste Local Plan.

Site 224 – Ambrose Quarry, Ewelme

Site Information (as nominated in 2009) Site Location Ambrose Quarry, Ewelme

Grid Reference SU 656892

Administrative Area South Oxfordshire

Parish Nuffield

Site Nominee(s) Grundon Waste Management Ltd.

Proposed Landfill for inert waste Development

Site Area 2.1 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Former quarry

Access Existing access onto Old London Road (within 500m of A4130)

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is a former mineral extraction site. (Policy W4 and W6) • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. • The site lies within 600m of the Oxfordshire Lorry Route Network (A4130). • The site lies within an AONB. • The site does not lie within 200m of a SAC. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site lies within 500m of ancient woodland to the south west. (Policy C7) • Site does not lie within 1km of SSSI or Natura 2000 site. Landscape / Visual (Policy C8) • Site lies within Chilterns AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • The Environment Agency advise that the site is located on a Principal aquifer and private water supplies are located nearby. This is a potential groundwater quality issue that might need to be risk assessed prior to the development. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies within 1km of Grade II listed building to the north west, although HGVs likely to access A4130 via the south east. • No impact on historic character expected. Transport and Access (Policy • Bus stops lie within 300m to the south east. C10) • May have impact on AM peak congestion (A4130). • Site lies in proximity to area with history of RTIs. • No works required to improve access to site. Public Rights of Way (Policy C11) • Restricted byway runs along the northern. boundary, however, site is unlikely to be impacted. Health and Amenity (Policy C5) • Residential properties lie within 250m to the south east. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within two aerodrome safeguarding areas. M10)

Cumulative Impact (minerals and • Site lies within 3km of three existing waste sites Ewelme No. 1, Ewelme No. 2 and Mains Motors, Woodside.

waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of three nominated waste sites: 013 Ewelme No. 2 Site, 138 Woodside, Old Henley Rd and 152 Ewelme No. 1 Site. • Site lies within 3km of a nominated minerals site: SG-61 Mains Motors.

Conclusion

The site lies within 600m of access onto the Oxfordshire Lorry Route Network, the A4130. The route is accessed via Old London Road a single carriageway which does not provide pedestrian walkways and is subject to a national speed limit restriction. A number of residential properties are located at the junction to both of these routes. There maybe potential for cumulative impacts to arise should the site be allocated which will require further assessment.

The site does not lie within a suitable distance to any urban area as identified within Policy W4 and lies within an AONB.

As a former extraction site, in accordance with the supporting text to Policy W6 the site has potential to accept inert wastes as part of restoring the County’s exhausted mineral workings. The site should therefore be considered further as part of the detailed assessment, however there appears to be limited opportunities for wider wastes uses.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 224 Site Name: Ambrose Quarry

Stage 1b: Detailed Assessment

PLANNING HISTORY

Ambrose Quarry is a partly worked now dormant quarry and has a planning permission for the extraction of chalk for agricultural use with an estimated 200,000 tonnes of mineral reserve remaining available. Under the extant planning consent – permission MW.002/56 dated 29/03/1956 and ROMP determination of new conditions MW.002/99a dated 10/02/1999 – extraction should cease by 2042 and the site be restored by 2044.

In 2012, planning permission was granted (retrospectively) to allow the use of the site for the storage of empty skips and containers for a temporary period of 3 years – application MW.0156/12, permitted 06/12/2012.

The period of time allowed for this skip storage has been extended, most recently by current permission MW.0121/18, dated 24/01/2019, which allows use of the land for the storage of skips to continue until 31.12.2021.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site comprises previously developed land as a former mineral working and therefore complies with Policy W5. However, it should be noted that the site lies within the Chilterns AONB and would only be acceptable if adequate and appropriate measures to mitigate adverse impacts on landscape could be provided (see Policy C8).

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Magpie Wood Ancient Woodland is located 330m to west which is considered to be an irreplaceable habitat. Further woodland is adjacent to the site.

There are no records of European protected species. Records of protected or notable species include several plant and invertebrate species. No significant ecological impacts are anticipated should this site be allocated for waste management uses.

The site is within Chilterns Escarpment Central Conservation Target Area (CTA) and therefore restoration of the site in line with the objectives of the CTA would be beneficial.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site comprises a relatively small former quarry site in the Chilterns AONB set in a wider landscape context of former quarries, waste recycling and open agricultural fields with hedgerows. The proposal development to infill the site with inert waste would be temporary and form part of the restoration process to restore the former quarry. Additional impacts on landscape character and views are not expected and restoration offers opportunities to deliver landscape benefits in the medium term.

A public right of way runs alongside the northern boundary with potential occasional glimpsed views into the site. Site appears to be quite well screened from Old London Road but noise and activity might influence experience and perception.

Traces of earlier historic landscapes are likely to have been removed as result of mineral extraction at the site. No impact on historic character of the landscape is therefore expected.

Compliance with Policy C10: Transport - Highways Officer Assessment

Old London Road already serves the Grundon Waste site to the North of Beggarsbush Lane and HGVs route south onto the A4130, which is suitable for HGV traffic. The Crowmarsh roundabout to the west along the A4130, towards Wallingford is placed under significant pressure during the AM and PM peak hours.

Access out onto Old London Road will likely need upgrading to cater for the uplift in HGV traffic.

Conclusion

The Core Strategy Policy W6 states that priority will be given to the use of inert waste that cannot be recycled as infill materials to achieve the satisfactory restoration and after use of inactive or unrestored quarries. Policy C8 states that great weight will be given to conserving the landscape and scenic beauty of AONBs and high priority will be given to the enhancement of their natural beauty.

On this basis and having regard to the site’s current state as an unrestored mineral site in the Chiltern AONB, it is considered that the allocation of the site for infill with insert waste is likely to result in a positive environmental benefit through the restoration of the site to deliver landscape benefits and offering potential opportunities for beneficial after use.

As the site is within relatively close proximity to existing and nominated waste sites, consideration will need to be given to potential cumulative impacts should this site be allocated.

RECOMMENDATION

It is considered that this site may be suitable for allocation having regard to potential cumulative impacts at the end of the site appraisal process.

Site 229 – Shellingford Quarry, Stanford in the Vale

Site Information (as nominated in 2016) Site Location Shellingford Quarry, Stanford in the Vale Grid Reference SU 325 938

Administrative Area Vale of White Horse

Parish Shellingford and Stanford in the Vale Site Nominee(s) Multi Agg Ltd

Proposed Recycling centre for inert Development and construction waste

Site Area 3.5 ha

Existing capacity Unknown

Annual Throughput 80,000 tpa (2007) 80,000 tpa (2006)

Existing land use Quarry and landfill and recycling site for inert waste Access Existing access onto A417

Current levels and Unknown types of traffic movement

Stage 1a: High Level Assessment TO BE REVIEWED PENDING BOUNDARY CHANGE

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • The site lies adjacent to the Oxfordshire Lorry Route Network (A417). • The site does not lie within an AONB • The site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • The site overlies the Shellingford Quarry Local Geological Site. (Policy C7) • Shellingford Crossroads Quarry SSSI lies approximately 200m to the north of the site. • Site lies within 500m of Ancient Woodland. • Site located in excess of 5km from International / European designated sites. • Site does not lie in close proximity to an LNR or NNR, but the Chimney Meadows NNR is within 6.5km of the site, to the north. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site located within 500m of Shellingford Conservation Area. • There are listed buildings within 1km of the site to the south west and north west. • There are no archaeological constraints as site is a former quarry, therefore any archaeological features will have been removed. • There are currently no known historic landscape constraints. Transport and Access (Policy • The A417 is adjacent to the site. C10) • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies within 150m of a fatal RTI on the A417, within 1km of two slight RTIs on the A417 and within 2.5km of three serious RTIs (2 on the A417 and 1 on the B4508). Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • The closest residential dwellings lie within 300m north-west of the site. Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site does not fall within aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Chinham Farm and Stanford in the Vale HWRC. waste sites) • Site lies within 3km of three existing minerals sites: Chinham Farm Quarry, Hatford Quarry and Faringdon Quarry. • Site lies within 3km of three nominated waste sites: 283 Hatford Quarry Extension, 230 Chinham Farm and 281 Faringdon Quarry. • Site lies within 3km of eight nominated minerals sites: SS-03/CR-17 Hatford Quarry, South extension, SS-07/CR-24 Home Farm, SS-08/CR-16 Shellingford Quarry Western extension, SS-12/CR-12 Land at Chinham Farm (Chinham Hill), SS-15/CR-11 Hatford Quarry North extension, SS-16/CR-21 Hatford Quarry Stanford Extension, SS-18/CR-22 Hatford Quarry West extension and SS-19/CR-23 Home Farm Carswell.

Conclusion The site does not lie within a suitable distance to the any areas as identified within Policy W4. However, the site benefits from direct access onto the Oxfordshire Lorry route Network (A417). The site is in close proximity to Hatford Quarry and Chinham Farm and a large number of nominated sites therefore cumulative impacts would need to be considered. Further consideration would also need to be given to potential impacts on the Conservation Area.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No:229 Site Name: Shellingford Quarry, Stanford in the Vale

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

Quarrying of sand and limestone and restoration by infill with inert waste at the existing Shellingford Quarry was originally permitted in 1986. The current quarrying and infill operations were permitted on 27th August 2009 (MW.0132/09).

‘Storage and exportation of sorted inert material’ (including recycling of inert waste to produce secondary aggregate for sale off site) permitted 8th October 2009, MW.0161/09; proposed throughput 60,000 tpa. Conditions required: • No aggregates to be imported to site after completion of sand extraction or by 31st December 2019, whichever is earlier; • Site to be restored within one year of completion of mineral extraction and landfill or by 31st December 2021, whichever is earlier. This is the currently active permission for recycling at Shellingford Quarry.

Permission MW.0132/09 for quarrying and infill was varied by a new permission granted on 28th April 2011, MW.0020/11. This is the current operative permission. The application included the statement: ‘The company operates a plant for the recycling of construction and demolition materials within the quarry and this will be unaffected by the proposals.’ Conditions require: • Cessation of mineral extraction, importation of aggregates and deposit of waste by 31st December 2028; and completion of restoration of the site by 31st December 2029; • Access only via existing quarry access onto the A417; • HGV movements limited to 200 per day (100 in, 100 out). This permission does not extend the period for recycling operation permitted by MW.0191/09.

An eastern extension to Shellingford Quarry was also permitted on 28th April 2011, MW.0021/11. Conditions require: • Cessation of mineral extraction and deposit of waste by 31st December 2020; and completion of restoration of the site by 31st December 2021; • Access only via existing quarry access onto the A417;

• HGV movements limited to 200 per day (100 in, 100 out).

The eastern extension area has been worked out and remaining mineral reserves in the main quarry area are low; the site promotor states that there is less than one year of available reserves.

Current planning application MW.0104/18 proposes mineral extraction and infilling with imported inert materials within most of the area of the nominated site (the northernmost part of the nominated area is not included), as a western extension to the existing Shellingford Quarry. It is proposed to extract 1.8 mt of limestone and 1.0 mt of sand over a 22 year period to 2041, at a maximum rate of 135,000 tpa; and infill and restore the excavated area with 1.6 m m3 of inert waste. The existing quarry access to the A417 and the processing plant within the existing quarry are proposed to be used (subject to a separate application for retention of the plant etc being submitted and approved). The application does not include continuation of the recycling operation permitted by MW.0161/09.

The Council’s Planning and Regulation Committee on 15th July 2019 resolved that, subject to legal agreements on long term aftercare and lorry routeing, permission be granted for this application.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There is irreplaceable habitat (ancient woodland) approximately 600m to the site. Notable habitats include a woodland belt along the southern site boundary.

Records exist for European protected species namely, Great Crested Newt and several bat species. Other protected / notable species include numerous bird species including Barn Owl, as well as Otter, Badger, Brown Hare and Water Vole.

The site is partly located within West Oxon Heights, Streams, Hills, Woods and Parks Conservation Target Area (CTA).

Site currently in use as an active quarry operation and therefore anticipated biodiversity impacts are considered low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It has consent as an existing landfill site; future restoration offers opportunities to enhance local landscape character.

Quarrying will have removed all traces of earlier landscapes.

Landscape impacts are considered to be low due to the existing use of the quarry, the existing permission for inert waste processing and the temporary nature of the development. Future restoration offers opportunities to enhance local landscape character reducing the impact in the long-term.

There are no Public Rights of Way within or adjacent to the site but views from footpaths further away might exist. Glimpsed views from Faringdon Road (A417) might exist.

Compliance with Policy C10: Transport - Highways Officer Assessment

The HGV movements will be directly onto the A417, with the A420 to the north west. There are known capacity issues along the A420 around Faringdon and the A338 around Wantage.

The existing access onto A417 is suitable for continuing use and is unlikely to require any upgrading.

Conclusion

The site is an existing waste site with direct access onto the Oxfordshire Lorry route Network (A417). Impacts on landscape and biodiversity are anticipated to be low.

It is noted that the Council is minded to grant planning permission for further mineral extraction and infilling on the adjoining site to the south-west (MW.0104/18), subject to the completion of a legal agreement. The principle of waste management uses in the vicinity of this site is therefore considered to be acceptable.

RECOMMENDATION

Given that the site benefits from planning permission for waste management uses that is shortly to expire, that mineral extraction in the vicinity of the site is permitted until 2028 and there is a Committee resolution to grant planning permission for the western extension such that mineral extraction is likely to continue well beyond the plan period, it is recommended that the site is allocated in the Waste Local Plan for waste management uses.

Site Number: 236 – Sheehan Recycled Aggregates Plant (Dix Pit Complex), Stanton Harcourt

Site Information (as nominated in 2018)

Site Location Sheehan Recycled Aggregates Plant (Dix Pit Complex), Stanton Harcourt Grid Reference SP401051

Administrative Area West Oxfordshire

Parish Stanton Harcourt

Site Nominee(s) Sheehan Haulage & Plant Hire Ltd Proposed Non-Hazardous (C&I and Development MSW) Waste Recycling Inert (CDE) Waste Recycling including Recycled Aggregates Site Area 6.83 ha Existing capacity 175,000 tpa (granted on appeal 07.01.2019) Annual Throughput 100,000 tpa (2017) 100,000 tpa (2016) 100,000 tpa (2015) Existing land use Existing waste site (recycling plant) Access Existing access onto unnamed road (within 800m of B4449) Current levels and 40 – 80 HGVs types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 15km of Oxford. (Policy W4) • Site is located approximately 800m from access onto the Oxfordshire lorry network (B4449) • Site does not lie within AONB. • The site does not lie within 200m of a SAC • Site is currently in operation as a waste site. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site lies within Flood Zone 1. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • The site is predominantly within an area of Grade 2 agricultural land. Historic Environment (Policy C9) • The Devil’s Quoits (Scheduled Monument) lies 700m to the south east - Historic England noted potential for impact on setting. • Beard Mill and The Old Vicarage Listed buildings are located within 500m to the north of the site. • There are no archaeological constraints and no impact on historic character expected given that the entire allocation site has been extensively disturbed, and it sits within a wider area of waste operations. • There are no known historic landscape constraints.

Transport and Access (Policy • Site is located approximately 800m from the Oxfordshire lorry network (B4449) C10) • There are no local transport connections. • No AM peak or PM peak traffic congestion identified within proximity to site. • There is no RTI history within 3km of the site. • Site is currently in operation as a waste site.

Public Rights of Way (Policy C11) • A bridleway appears to run within the western boundary of the site, but not within the main site area. • A Public Right of Way runs along the northeastern boundary of the site; occasional views of workings likely to be possible. Health and Amenity (Policy C5) • Beard Mill (residential) is located 500m to the north west of the site. Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site is located within the RAF Brize Norton aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of four existing waste sites: Lakeside Industrial Park, Rear of Cemex Batching Plant, Dix Pit and waste sites) Gill Mill Quarry. • Site lies within 3km of two existing minerals sites: Stanton Harcourt Quarry (Stonehenge Farm) and Gill Mill Quarry. • Site lies within 3km of two nominated waste sites: 003 Dix Pit and 103 Land at Lakeside Industrial Estate. • Site lies within 3km of eight nominated minerals sites: SG-14 Stonehenge Farm, SG-18 Land near Standlake, SG- 27 Vicarage Pit, Cogges Lane, SG-28 Guy Lakes North, adj B4449, SG-29 Sutton Farm, SG-30 Home Farm, Brighthampton, SG-31 Land east of Sutton and SG-36 Land at Friars Farm.

Conclusion

The site currently operates as an existing waste site processing around 100,000 tpa. The site lies within 15 km of Oxford and is therefore potentially suitable to provide small-scale, non-strategic and strategic waste management capacity in accordance with Policy W4.

The site lies approximately 800m from access onto the Oxfordshire Lorry Route Network (B449). Access to this route is via an access route which does not provide pedestrian walkways, although is subject to a 20 mph speed limit restriction.

Given its proximity to a Scheduled Monument, any further development on the site would need to be appropriately mitigated to avoid harm to its setting. Potential cumulative impacts will need to be considered further.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 236 Site Name: Sheehan Recycled Aggregates Plant (Dix Pit Complex), Stanton Harcourt

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The site has an extant planning consent for a C&D recycling facility with a capacity of 175,000 tpa with an end date of 2029.

The original permission was granted on appeal on 23rd March 2011 (MW.0091/09). Most recent, and currently operative permission granted on appeal on 7th January 2019, MW.0073/17 (APP/U3100/W/18/3196658). Conditions limit capacity to maximum 175,000tpa; and require cessation of operation by 31st December 2029 and restoration of site by 31st December 2030.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known irreplaceable habitats within or adjacent to the site. Numerous waterbodies surround the site including the River Windrush. Records exist for several European Protected Species within or adjacent to the site including Great Crested Newt and several bat species. Records also exist for several notable or protected species including Barn Owl, Otter, Badger, Brown Hare and Water Vole and numerous birds.

The site is 1.1km from the Stanton Harcourt geological SSSI and within the Lower Windrush Valley Conservation Target Area (CTA) adjacent to the Dix Pit Local Wildlife Site and proposed extension.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting and is an existing site within an area of quarrying / waste recycling and restored gravel pits.

No additional landscape and visual impacts expected. However, if the site is allocated for a permanent use, there would no longer be opportunities to deliver landscape benefits through restoration.

Increase in capacity and resulting increase in HGV movements has the potential to indirectly impact on the wider landscape area.

Compliance with Policy C10: Transport - Highways Officer Assessment The site has good existing access to unnamed road.

HGVs will be routed to the B4449 (Freight Priority Network - Tertiary) at Stanton Harcourt, then 7.3km to A40.

There have been problems with HGVs through Sutton village on B4449. Not all HGVs will go this way. Routing agreement already in place restricting movements at certain times via Sutton.

Conclusion

There are no in principle reasons for preventing future waste management uses on the site that could not be overcome with appropriate mitigation. However, the site already benefits from an extant consent that runs until 2029 and its allocation would therefore not make a significant additional contribution towards meeting Oxfordshire’s waste management needs.

There are a number of existing and nominated minerals and waste sites in the vicinity of this site and therefore cumulative impacts would need to be considered.

RECOMMENDATION

As the site has planning permission until 2029 and given that Core Strategy Policy W11 already safeguards such operational waste management sites, allocation of the site in the Local Plan is not going to make a significant additional contribution to meeting waste management needs. It is not therefore recommended that the site is allocated in the Local Plan.

Site 245: Challow Marsh Farm, West Challow

Site Information (as nominated in 2008) Site Location Challow Marsh Farm, Circourt Road, East Challow

Grid Reference SU367900

Administrative Area Vale of White Horse

Parish East Challow

Site Nominee(s) McDowell Trading Ltd

Proposed Inert soils and aggregate Development Site Area 6.37 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Greenfield/Previously developed

Access Access onto Circourt Road (within 550m of A417)

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Site Name Challow Marsh Farm Site ref 245 Criterion Comments / Justification Score Compliance with Waste Strategy • The site lies within 5km of the nearest large town (Wantage and Grove). (Policy W4) • The site lies approximately 550m from access onto the Oxfordshire lorry route network (A417). • The site is not located in the Chilterns AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is located within 3km of an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • Hill Farm House and Stable and Coach House (Grade II Listed) lie 300m to the south west of the site. • No identified archaeological constraints. Transport and Access (Policy • Circourt Road is subject to a weight restriction (7.5T). C10) Deal with only at detailed • Poor access to public transport connections. stage? • No AM peak or PM peak traffic congestion identified within proximity to site.

Public Rights of Way (Policy C11) • No public rights of way in proximity to the site area. Health and Amenity (Policy C5) • There are residential properties within 500m to the west and east of the site. Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site is not located within aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of one existing waste site: Grove Industrial Park.

waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

This greenfield site was nominated in 2008. It lies within 5km of Wantage and is therefore in an area which is deemed suitable to provide non-strategic and small-scale waste management capacity in accordance with Policy W4. Due to the time elapsed since this site was nominated, there is uncertainty over its availability.

The site lies within 600m of access onto the A417 to the south via Circourt Road which restricted for use by vehicles weighing under 7.5 tonnes.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 245 Site Name: Challow Marsh Farm, West Challow

Stage 1b: Detailed Assessment

PLANNING HISTORY

No planning history.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site comprises a field that has in part been previously developed. To conform with Policy W5, proposals for waste management at this site will need to demonstrate that the site is the most suitable and sustainable option. The supporting text to Policy W5 indicates that sites in a rural location, such as this, may be appropriate for composting and biological treatment.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known records of Irreplaceable Habitats or Notable Habitats within or adjacent to the site. Records exist for European protected species including Great Crested Newt and several bat species. Records also exist for several protected/notable species including numerous bird species, Barn Owl, Otter, Badger, Brown Hare and Water Vole.

Overall impacts are considered likely to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape but is located approximately 2.5km from North Wessex Downs AONB. The site is of small scale, its use for the purposes of waste management would in principle be unlikely have an adverse impact on the AONB.

The surrounding area is predominantly a flat landscape set in the context of regular agricultural fields of varying sizes with hedgerow boundaries and hedgerow trees. Boundary vegetation is low in places allowing views across fields. There are currently no known historic landscape constraints. The

general character of the site reflects the wider local character of the area.

Although the site is small, its use for permanent waste management facilities will result in an isolated development in the landscape introducing noise and activity into a tranquil area causing a moderate impact on the local landscape character.

Some views of the site may be possible form Circourt Road. The planting of native hedgerows along the front of the site could assist in mitigating visual impacts.

Compliance with Policy C10: Transport - Highways Officer Assessment

Circourt Road has a 7.5t weight restriction, due to the rail bridge crossing further to the north. The road is not suitable for two way HGV traffic and would need significant widening and verge improvement. Visibility splay of 160m cannot be achieved in the southerly direction at Circourt Road/A417 junction.

A417 is a strategic route and is known to have capacity issues in the peaks. There are known capacity issues along the A420 around Faringdon and the A338 around Wantage.

Conclusion

Whilst the site could be well screened and is in principle well located to serve the waste management needs of Wantage and Grove, it is not considered suitable for waste management uses given the highway restrictions and its relatively isolated location.

RECOMMENDATION

It is not recommended that the site is allocated in the Site Local Plan.

Site 249B – High Cogges Farm, Witney Site Information (as nominated in 2009)

Site Location High Cogges Farm, Witney

Grid Reference SP380095

Administrative Area West Oxfordshire

Parish South Leigh

Site Nominee(s) High Cogges Farm Partnership Proposed Anaerobic digester for food Development waste, farm wastes (manures) and potentially crops Site Area 2.3 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Green field

Access Access onto S Leigh Road (within 1km of A40) Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is located within 5km of Witney, and within 20km of Oxford. (Policy W4) • The site is located 1.1km from access to the Oxfordshire Lorry Route Network (A40). • Site is not located within AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within an AQMA. • Natural England advise the site may require further assessment in terms of air pollution effects on Ducklington Mead SSSI, depending on the energy input into the anaerobic digester. Soil Resources (Policy C6) • Site within an areas of Grade 3 and Grade 4 agricultural land. Historic Environment (Policy C9) • Ladymead Cottage is located 200m to the south west of the site. • Site contains no archaeological features. Transport and Access (Policy • Prior to access onto the Oxfordshire Lorry Route Network (A40), access would likely be via C10) South Leigh Road which is a single-track road with no pedestrian walkways and soft verges. • South Leigh Road is signed as being unsuitable for heavy goods vehicles. This then leads onto the B4022 which provides access to the A40. • Possible AM peak or PM peak traffic congestion identified within proximity of site. • Site lies in close proximity to area with history of RTIs. Public Rights of Way (Policy C11) • No public rights of way overlie the site. Health and Amenity (Policy C5) • Residential properties within 500m to the south of the site along South Leigh Road however it is expected that vehicle movements will not have a limited impact upon health and amenity as access will be taken to the north via the A40. Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site falls within the RAF Brize Norton and London Oxford Airport aerodrome safeguarding M10) sites.

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Gill Mill Quarry and T&B Motors. waste) • Site lies within 3km of an existing minerals site: Gill Mill Quarry. • Site lies within 3km of a nominated waste site: 249A High Cogges Farm. • Site lies within 3km of a nominated minerals site: SG-23 Windrush North, Gill Mill.

Conclusion

The site does not operate as an existing waste site. Its current strategic value is therefore unknown at this stage.

The site is a greenfield site and appears to be in use for agricultural purposes. The site lies within 5km of Witney. The site is therefore suitable in terms of scale and proximity to these areas to provide non-strategic and small-scale waste management capacity in accordance with Policy W4.

The site is located 1.1km from access to the Oxfordshire Lorry Route Network (A40). Prior to access onto the Oxfordshire Lorry Route Network (A40), access would likely be via South Leigh Road which is a single-track road with no pedestrian walkways and soft verges. South Leigh Road is signed as being unsuitable for heavy goods vehicles. This then leads onto the B4022 which provides access to the A40.

There are residential properties within 500m to the south of the site along South Leigh Road however it is expected that vehicle movements will have a limited impact upon health and amenity as access will be taken to the north via the A40.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 249B Site Name: High Cogges Farm, Witney

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

New site. No planning history.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site comprises greenfield land. Proposals for waste uses on this site would therefore need to demonstrate that the site is the most suitable and sustainable option for the proposal to conform with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known records of irreplaceable habitats within or adjacent to the site. Notable habitats within or adjacent to the site include coniferous woodland along the southern boundary of the site.

There are European protected species within or adjacent to the site, namely Great Crested Newt and several bat species. Other protected / notable species include numerous bird, amphibian, mammal and invertebrate species.

Overall impacts are considered likely to be low. Site restoration / off-site enhancements will need to ensure a net gain in biodiversity is achieved.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It forms part of an arable field bounded by a stream and hedgerows with trees. Rural landscape context of fields, hedgerows and tree lined small watercourses. Landscape that feels intact and tranquil despite noise from the A40.

Access currently narrow and well screened but likely to require widening and removal of characteristic vegetation.

Large structure and activity are expected to be visible in selected views from public vantage points such as the slip road and South Leigh Road. Mitigation planting has potential to assist in mitigating impact on views but is unlikely to be fully effective.

The allocation comprises a new permanent development on a greenfield site that will introduce large structures and activities into an agricultural landscape that is considered sensitive in landscape character terms. Impacts on views from public vantage points are likely to be moderate.

Overall the landscape and visual impact is considered substantial due to the permanent and isolated nature of the development, the site being a greenfield site and the sensitive rural landscape context.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site has good access to the A40 east of Witney only (via Shores Green junction)

Conclusion

The site is a greenfield site in a sensitive rural context. Although the landscape is undesignated, use of the site for waste management uses would have an adverse landscape and visual impact. However, given the proximity of the site to the A40, its location close to Witney and with appropriate mitigation, it is considered that the site could play a role in meeting the waste management needs of the county

RECOMMENDATION

It is recommended that the site is allocated in the Local Plan for a small scale, not strategic facility.

Site 261 – The Marshes, Knightsbridge Farm, Yarnton Site Information (as nominated in 2018)

Site Location The Marshes, Knightsbridge Farm, Yarnton

Grid Reference SP487122

Administrative Area West Oxfordshire

Parish Yarnton

Site Nominee(s) Sheehan Haulage and Plant Hire Ltd Proposed Non-Hazardous (C&I and Development MSW) Waste Recycling

Site Area 3.3 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Northern part of site appears to be greenfield. Southern part appears to be used for the storage of containers.

Access Existing access onto A44

Current levels and N/A type of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site lies within 15km of Oxford. (Policy W4) • Site is accessed directly via the Oxfordshire Lorry Route Network (A44) and lies approximately 1.3km to the west of a junction providing access onto the A34. • The site does not lie within an AONB. • The site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Oxford Meadows SAC is approximately 1.4km to south of the site (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species (Rushy Meadows SSSI 1.7km north and Pixey and Yarnton Meads SSSI, 1.4km south). • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Small area of FZ2/3 to the north of the (Policy C3 and Policy C4)) site. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • The Grapes Inn, Grade II Listed building is located 300m to the west of the site. • Quainton’s Cottage, Grade II Listed, is located 350m to the west of the site. • No known archaeological constraints. Transport and Access (Policy • There is a bus stop within 500m of the site access. C10) • No AM peak or PM peak traffic congestion identified within proximity to site. • The area has a minimal RTI history, no ‘serious’ or ‘fatal’ incidents within 3km. Public Rights of Way (Policy C11) • No public rights of way within the vicinity of the site. Health and Amenity (Policy C5) • There is a residential property just over 100m to the south of the site. Green Belt (Policy C12) • Site is located in the Green Belt. Aerodrome Safeguarding (Policy • Site falls within the London Oxford Airport aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Worton Farm and Charlett Tyre Yard. waste sites) • Site lies within 3km of an existing minerals site: Cassington Quarry.

• Site lies within 3km of a nominated waste site: 009 Worton Farm (Areas C & D). • Site lies within 3km of three nominated minerals sites: SG-04 Land at Mead Farm, SG-05 Land to the East of Cassington Quarry and SG-16 Land at Stonehouse Farm.

Conclusion

This site is within the Oxford Green Belt. Development within the Green Belt would be inappropriate unless it would involve the replacement of a building, providing the new building is in the same use and not material larger than the one it replaces (NPPF 145).

The north east of the site appears to be open countryside. The south west of the site appears to be used for container storage and other uses in association with Sheehan Haulage and Plant Hire. The site lies within 15 km of Oxford and is therefore in principle suitable to provide strategic, non- strategic or small-scale waste management capacity.

The site is accessed directly onto the Oxfordshire Lorry Route Network (A44) with further access onto the A34 within 1.8km to the A34 to the east of the site.

It is considered that the site should be taken forward for further detailed assessment having regard to NPPF that development must preserve the openness of the Green Belt and not conflict with the purposes of including land within it (with reference to paragraph 134).

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 261 Site Name: The Marshes, Knightsbridge Farm, Yarnton

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview Awaited

Previous applications for waste operations at this site and on adjacent land have been refused including proposed development for the erection of waste recycling and transfer facility and access improvements (MW.0103/13, refused 14.01.2014), and subsequent appeal dismissed on 23.03.2015 (APP/U3100/A/14/2221906), principally on Green Belt grounds.

There were two earlier proposals for waste management development on adjacent land, to the south west – The Gullet, which were refused in 1994; and appeals were dismissed in 1995; principally on green belt grounds.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The southern section of the site partly overlies land used to store containers while the northern section of the site overlies greenfield land. The site lies adjacent to other waste and industrial uses encouraging both synergy and the potential for reduced vehicle movements. The site does not lie within an AONB and demonstrates direct access onto the A44. The site is therefore considered be a potentially sustainable option for future waste use.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no records of Irreplaceable Habitats or Notable Habitats within or adjacent to the site. Records for European protected species include Great Crested Newt and several bat species. Other protected and Notable species records include numerous birds, amphibian, mammal and invertebrate species.

The Wolvercote Meadows SSSI and Pixey & Yarnton Meads SSSI within 2km. There are also several Local Wildlife Sites within vicinity of site, the closest being Meadows West of the Oxford Canal, approximately 300m to east of site. The Lower Cherwell Valley Conservation Target Area is approximately 250m to east.

Overall impacts are considered likely to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is on the outskirts of Yarnton and is located between light industrial uses and a solar farm which reduces its sensitivity in landscape terms. Development at this site is likely to have limited impact on local landscape character. The site is visually well contained by existing mature boundary features and there are no public vantage points that offer views into the site apart from along the access road. The existing mature boundaries of the site would need to be maintained. There is a proposal for a multi-user route between Kidlington to Yarnton through fields to north however views, particularly of the site, particularly during the summer month, are likely to be very limited.

There may be the potential for development to impact on the historic landscape character of the area and any development would need to seek to preserve historic boundary features.

Overall the development is not expected to cause additional landscape and visual impacts subject to existing mature vegetation, including boundary vegetation being retained.

Compliance with Policy C10: Transport - Highways Officer Assessment

The existing access to the site is good and is straight on to A44 (part of Oxfordshire lorry route network). The A44 does not pass through any villages.

In dismissing the appeal 23.03.2015 (APP/U3100/A/14/2221906), the Inspector concluded that the effect of the scheme on the safety and convenience of highway users would be acceptable however concerns were raised at the time in relation to the existing junction off the A44 and potential need for junction modifications to prevent vehicles turning right into or out of the site. Since the appeal there have however been two recorded damage-only shunt collisions due to queuing traffic behind a vehicle turning right into the site and there may have be many other unrecorded collisions. Modification to the junction to allow left in and left out only may therefore assist to maintain safety and convenience for highway users and these works are likely to be deliverable.

Conclusion

There is a history of planning refusals on this site, including at planning appeal. The site is partially previously developed but much of the site is greenfield. It is considered unlikely that very special circumstances would be able to be demonstrated for the release of this site to meet Oxfordshire’s waste management needs. The development of the site would lead to encroachment of the countryside which would be contrary to one the five purposes that the Green Belt serves, as set out in NPPF.

The allocation of this site should therefore only be considered where the benefits of the proposal would clear outweigh other considerations. As such it is necessary to demonstrate that there are no other more suitable and sustainable alternatives to meet the County’s waste management needs.

RECOMMENDATION

The site would be inappropriate development in the Green Belt and should not be allocated unless there are exceptional circumstances to justify its release.

Site 274 – Moorend Lane Farm, Thame Site Information (as nominated in 2018)

Site Location Moorend Lane Farm, Thame

Grid Reference SP710068

Administrative Area South Oxfordshire

Parish Thame

Site Nominee(s) David Einig Contracting Ltd

Proposed Inert (CDE) Waste Recycling Development including Recycled Aggregates

Site Area 4.75 ha

Existing capacity 130,000 tpa

Annual Throughput Unknown

Existing land use Existing quarry and waste site (inert waste landfill).

Access Existing access onto Moorend Lane (within 200m of A4129)

Current levels and Average 18 HGV movements types of traffic per day movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site manages over 50,000 tpa and is therefore considered to be a strategic waste (Policy W4) management facility pending restoration of landfill site in 2022. • However, the site lies over 15km of site and lies within 2km of Thame. Therefore, the site is considered suitable for non-strategic and small-scale waste activities in accordance with Policy W4. • Site lies 170m from access to the Oxfordshire Lorry Route Network (A418). • Site is not located within AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. • Site located in excess of 500m from a SINC or LNR (Cuttle Brook). Landscape / Visual (Policy C8) • Site is not located within AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Flood zone 3 lies north of the site. Air Quality (Policy C5) • Site not located within an AQMA. Soil Resources (Policy C6) • Site lies within Grade 5 BMV agricultural land. Historic Environment (Policy C9) • Site lies within 1km of Thame Conservation Area to the south-west. • Site has been extensively disturbed by previous development as such there are no archaeological constraints to this allocation site. • There are currently no known historic landscape constraints. Transport and Access (Policy • Prior to access onto the Oxfordshire Lorry Route Network (A418), access would likely be via C10) Moorend Lane which is a single track road with no pedestrian walkways and soft verges. • This then leads onto the A4129 which is a single carriageway on the edge of Thame and immediately adjacent to publicly accessible open space. • The site lies within 400m from a bus stop. • Site does not lie within close proximity to area within an area known for traffic congestion, but PM congestion along the A418, north of Thame is evident. • Site lies with close proximity of area known for serious and fatal RTI’s.

• Site is an existing waste site. No works to access required. Public Rights of Way (Policy C11) • A footpath lies adjacent to and crosses the site with direct views of it. • Important footpath link between Thame and Haddenham & Thame Parkway station. Health and Amenity (Policy C5) • Site is within 250m of a residential property and publicly accessible open space. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Cumulative Impact (existing • Site lies within 3km of one existing waste site: Menlo Business Park (ASM). minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of a nominated waste site: 279 Rear of Ford Dealership. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site currently manages over 50,000 tpa and is therefore considered to be a strategic waste management facility, however it should be noted that restoration of the site is required by 2022. The site lies over 15km from Oxford and over 5km from any large town. However, the site lies within 2km of Thame and is therefore considered suitable for non-strategic and small-scale waste activities in accordance with Policy W4.

Site lies 170m from access to the Oxfordshire Lorry Route Network (A418). Prior to access onto the Oxfordshire Lorry Route Network (A418), access would likely be via Moorend Lane which is a single track road with no pedestrian walkways and soft verges. This route then leads onto the A4129, a single carriageway on the edge of Thame and immediately adjacent to publicly accessible open space.

There is limited potential to further intensify waste management activities although there may be potential for the site to provide a diversification of waste activities.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 274 Site Name: Moorend Lane Farm, Thame

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The site is an existing operational landfill site. The approved restoration for the site is infill to level with the soils replaced and returned to arable agricultural land.

Importation of inert material to restore the old landfill and sewage beds and extraction of small sand reserve originally permitted 31st January 2013 (MW.0101/12). A number of S.73 applications have been permitted which have varied the original permission, in particular to extend the end date for operations. The most recent permission granted on the 15th June 2018 (MW.0009/18) requires that extraction of minerals shall cease by 31st December 2020 and the site be restored by 31st December 2022.

There is an adjacent site with permission for the infilling of land to create a full-sized football pitch and two smaller football pitches at Thame Football Partnership Meadow View Park, Meadow View Park, Thame OX9 3RN (MW.0045/17). This has not yet been implemented.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats or notable habitats within or adjacent to the site. There are bats (European protected species) in the local area. Other protected/notable species include Badger, Brown Hare, Hedgehog and birds.

Cuttle Brook Local Nature Reserve lies approximately 1km to south-west.

There is likely to be a loss of Green Infrastructure on the existing waste area if the site is not restored.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. The character or setting of settlement is not affected.

The site is viewed in context of football stadium and sewage works reducing sensitivity of view.

Compliance with Policy C10: Transport - Highways Officer Assessment

The A4129 is the main perimeter route around Thame, which connects with the A418, both of which are on the Oxfordshire Lorry network route. However, during the peak hours the two roundabouts (Rycote Lane and Aylesbury Road) have congestion issues.

The existing access is Moorend Road. Moorend Lane is currently not suitable for HGV traffic and two-way vehicular flow as it is opposite Cromwell Avenue, so there will be conflicting vehicular movements. This would need significant improvement works. The junction of Moorend Lane with the A4129 is on the inside of an elongated bend, therefore the required visibility splays of 120m look to be unachievable, as they cut across third party land.

Conclusion

The site is in existing waste management uses and would be viewed in the context of the adjacent sewage treatment works. The site is not within a designated landscape or its setting, there are no irreplaceable habitats or notable habitats within or adjacent to the site. Subject to appropriate mitigation of any local effects and assuming that any future waste management use does not operate more intensively than the current landfill site, it is considered an appropriate site for a small-scale facility.

RECOMMENDATION

It is recommended that the site is allocated for small-scale non-strategic waste management uses.

Site 276 – Oday Hill, Sutton Wick Site Information

Site Location Oday Hill, Sutton Wick

Grid Reference SU492950

Administrative Area Vale of White Horse

Parish Drayton and Sutton Courtenay

Site Nominee(s) Unknown

Proposed New waste site for C&I Development treatment and CDE recycling

Site Area 4.7 ha

Existing capacity Unknown

Annual Throughput Unknown

Existing land use Existing quarry

Access Existing access onto B4017 via Stonehill Lane Current levels and Unknown types of traffic movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 5km of Abingdon and Didcot and 15km of Oxford. (Policy W4) • Site lies 1.9km to the east of the Oxfordshire Lorry route Network (B4017). • Site does not lie within AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • The proposed site includes an area of land safeguarded for a strategic water storage reservoir and ancillary works in the adopted Vale of White Horse Local Plan 2031 Biodiversity and Geodiversity • Site does not lie within 5km of International / European designated sites. (Policy C7) • Site does not lie within or adjacent to ancient woodland. • Site does not lie within 1km of SSSI, NNR and protected species. • Site does not lie within 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within, or close to AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site is not located within, or close to AQMA. Soil Resources (Policy C6) • Site within an area of both Grade 1 and Grade 5 BMV agricultural land. Historic Environment (Policy C9) • There are no heritage assets within 1km. • The site has been extensively disturbed by previous development as such there are no archaeological constraints and no impact on historic character expected. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies 1.9km to the east of the Oxfordshire Lorry route Network (B4017). C10) • Poor access to nearby public transport. • Site lies in close proximity to areas subject to AM and PM traffic congestion on the B4017 and Ock Street in Abingdon. • Site lies within close proximity to area with history of serious RTI’s. • Narrow access to site via Stonehill Lane. Public Rights of Way (Policy C11) • The site lies adjacent to a public right of way on eastern boundary. • Another public right of way runs in east-west direction south of the site Health and Amenity (Policy C5) • Allotments lie adjacent to the north-western boundary of the site. • A number of residential properties align Stonehill Lane – the primary access route to the sites entrance. Green Belt (Policy C12) • The site is not located within the Green Belt.

Aerodrome Safeguarding (Policy • The site lies within the Dalton Barracks airport safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of five existing waste sites: Drayton HWRC, Sutton Wick Lane, Sutton Courtenay, Drayton waste sites) Depot and Milton Park. • Site lies within 3km of two existing minerals sites: Sutton Courtenay Quarry (Bridge Farm) and Sutton Wick Quarry. • Site lies within 3km of a nominated waste site: 010 Sutton Courtenay. • Site lies within 3km of a nominated minerals site: SG-67 Sutton Wick Quarry.

Conclusion

The site exists as an operational quarry and lies within 2km of the Oxfordshire Lorry Route Network (B4017). The site is accessed via Stonehill Lane, a single-track route subject to a 15-mph speed restriction. A number of residential properties lie adjacent to this route and should be a key consideration in promoting this site waste for development.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 276 Site Name: Oday Hill, Sutton Wick

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The site is currently an operational quarry with sand and gravel processing plant.

Site subject to planning permissions requiring restoration by 31st December 2028 (granted on 19th December 2018 MW.0099/18). Under the latest permission the processing plant is to be removed by 31st December 2025, extraction of sand and gravel from this site shall cease on or before 31st December 2027 and any buildings, plant and equipment be removed, and the site shall be fully restored by 31st December 2028.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities The site is an active mineral working and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment There are no irreplaceable or notable habitats within or adjacent to the site.

There are several bat species (European protected species) within and adjacent to the site. Records exist for several notable and protected species including Barn Owl, Brown Hare, Water Vole, Otter, Badger and numerous birds.

Thames Radley to Abingdon Conservation Target Area (CTA) is located approximately 1.3km to the north-east.

Limited GI opportunities at present, though may have some habitat value. Possible geodiversity interest.

The existing site is already subject to high levels of disruption therefore overall impacts are expected to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment Site is not within a designated landscape or its setting.

Existing quarry site South of Abingdon. Landscape context of former mineral workings, sewage works and former tip but also allotment gardens and town

park. Site partly screened but occasional or glimpsed views might exist from PRoW, allotment site or park.

Visual sensitivity reduced by current use.

In light of the current use of the site and the existing landscape context no increase in impacts on landscape character, visual impact or historic character is expected.

Compliance with Policy C10: Transport - Highways Officer Assessment

Access on to the B4017 is adequate however vehicles would have to route through Abingdon to the Marcham Interchange or across the Thames or south through Drayton to the Milton Interchange, through the Steventon lights. Both of these route experience peak hour congestion.

Information from District Council

Data from the District Council shows a gas pipeline runs along the south of the site. The consultation zone extends into the site. Any excavation work here will need to take account of the pipeline and its consultation zone.

Conclusion

As the site includes land that is safeguarded for the Wilts and Berks Canal and new reservoir infrastructure in the adopted Vale of the White Horse Local, Plan, long term use of the site beyond the currently permitted mineral working and processing, may prejudice the future implementation of the proposed reservoir and associated ancillary works.

RECOMMENDATION

Given the current safeguarding in the adopted Vale of the White Horse Local Plan, it is not recommended that the site is allocated in the Minerals and Waste Local Plan.

Site 278 – Land off the B4100, Baynards Green Site Information (as nominated in 2015)

Site Location Land off the B4100, Baynards Green, Ardley/Fritwell Grid Reference SP 539 295

Administrative Area Cherwell

Parish Ardley

Site Nominee(s) David Einig Contracting Ltd

Proposed Recycling operation for inert Development waste

Site Area 15 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Largely green field.

Access Existing access onto B4100 (within 800m of A43) Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. Site (Policy W4) lies adjacent to the Oxfordshire Lorry Route Network (B4100) which further connects to the A43 and M40 just over 1km to the east of the site. • The site appears to currently be in agricultural use. • The site does not lie in proximity of an AONB. • The site does not lie within 200m of a SAC. District Local Plan Allocation • The site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • The site does not lie within, or close to AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • The Environment Agency advise that the site is located on a Principal aquifer and private water supplies are located nearby. This is a potential groundwater quality issue that might need to be risk assessed prior to the development. Air Quality (Policy C5) • The site does not lie within, or close to AQMA. Soil Resources (Policy C6) • The site lies within an area of Grade 3 agricultural land. • The land is predominantly undeveloped, with the exception of the southern corner of the site. Historic Environment (Policy C9) • There are not heritage assets within or adjacent to the site. • There are no known archaeological constraints. Transport and Access (Policy • The site does not lie within 500m of public transport access. C10) • Site lies within close proximity to areas known for AM and PM traffic congestion (local roads around Baynards Green). • The site does not lie within area with history of RTI’s. Public Rights of Way (Policy C11) • There is a public footpath which bisects the site from the west to the east corner. Health and Amenity (Policy C5) • There are residential properties within 200m of the site to the north and east. Green Belt (Policy C12) • The site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • There is one existing waste site within 3km of the site: Ardley Landfill, ERF and HWRC. waste sites) • There are no existing minerals sites within 3km of the site. • There is one nominated waste site within 3km of the site: 287 Ardley Fields. • Site lies within 3km of a nominated minerals site: CR-15 Land off the B4100, Baynards Green.

Conclusion

The site is located in a remote, rural location and does not lie within a suitable distance to an urban area as identified within Policy W4. The site also overlies Grade 3 agricultural land, although the site area does not exceed 20 hectares.

The site does provide direct access onto the Oxfordshire Minerals and Waste Lorry Network (B4100) with relatively close connections to the A43 and M40 soon thereafter.

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 278 Site Name: Land off the B4100, Baynards Green

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site comprises greenfield land. Proposals for waste uses on this site should demonstrate that the site is the most suitable and sustainable option to conform with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no records of Irreplaceable Habitats and Notable habitats within or adjacent to the site Notable Habitats within/adjacent-None known.

Record of European protected species include bat species in the local area. Other protected and notable species include several records for Swifts, along with Badger, Hedgehog and several other birds.

The Ardley Cutting & Quarry geological SSSI is approximately 1.8km to south. The Tusmore & Shellswell Park Conversation Target Area is approximately 1.2km to north-east.

Potential loss of existing undeveloped GI resource as currently in agricultural use.

Overall impacts are considered likely to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Waste management uses on this site will result in isolated development in what is currently an agricultural landscape. The landscape sensitivity is however reduced by the proximity of detracting influences such as the M40 and B4100 which border the field on Western and Eastern side respectively.

The landscape character is one of an open plateau landscape with low hedges that allows long views in many places. The site is crossed by a public right of way and another public right of way runs along the eastern boundary of the site. Occasional views of the site from the B4100 and M40 exist.

There is likely to be no impact on historic landscape character.

In summary, the location of the site between M40 and B4100 reduces the landscape sensitivity but overall the landscape and visual impact of the proposal is considered moderate due to the large size of the allocation, the site being a greenfield site, the permanent nature of the development, and the site forming an isolated unrelated development in a predominantly agricultural landscape.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site access would be via an existing access to the B4100 (Freight Priority Network - Tertiary). The A43 is approximately 850m and the M40 2km. Baynards Green roundabout (A43 / B4100) does get very congested at peak hours but no towns or villages would be directly affected. Increased HGV trips and turning movements on the B4100 may also cause concern.

The existing access would require improvement including a right turn filter lane onto the B4100.

Conclusion

It is unlikely that this site will be found to be the most suitable and sustainable option for waste management uses given its remote countryside location and distance from larger and smaller settlements. Potential adverse impacts on the character of the landscape and the countryside generally, coupled with the potential requirement for highway improvements and concerns about the suitability of the B4100 for increased HGV traffic leads to a conclusion the site should not be allocated for waste uses.

RECOMMENDATION

It is recommended that the site is not allocated for waste management uses unless there are no other more suitable and sustainable site options.

Site 279 – Land rear of Ford Dealership, Rycote Lane, Thame Site Information (as nominated in 2015)

Site Location Rear of Ford Dealership, Ryecote Lane, Thame

Grid Reference SP690055

Administrative Area South Oxfordshire

Parish Thame

Site Nominee(s) David Einig Contracting Ltd

Proposed Recycling operation for C&D Development and screening of soils

Site Area 0.59 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Appears to be used for material storage. Access Existing access onto A329 (Rycote Lane) with parking and turning scheme

Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 2km of Thame and is approximately 15km from Oxford. (Policy W4) • The site lies adjacent to and provides direct access onto the Oxfordshire Lorry Route Network (A329) • Site is not located within AONB. • Site does not lie within 200m of a SAC. District Local Plan Allocation • The site does not conflict with a district local plan allocation. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies within 1km of Thame Conservation Area to the north-east. • There are a number of listed buildings within 1km of the site. The closest of which being Manor Farm approximately 700m to the west and properties on the edge of Thame approximately 600m to the east of the site. • Historic England advise that this site is potentially within setting of listed buildings at Manor Farm, the potential impact on which should be taken into account in deciding whether or not this site, or part of it, is suitable for waste management. • The site contains no archaeological features and as such there are no archaeological constraints. • There are currently no known historic landscape constraints; no impact on historic character expected.

Transport and Access (Policy • PM peak traffic congestion identified within proximity to site (along the A418 to the north of the C10) site).

• Site lies within 3km to area with history of RTIs – Thame Road to the north of the site and Oxford Road to the north east of the site. • The site lies to the rear of a car show room with existing access for heavy good vehicles and is not visible from the highway. Public Rights of Way (Policy C11) • No public rights of way within the site. Health and Amenity (Policy C5) • There is a residential property within 250m to the south of the site. • Properties lie within 500m of the site to the east. Green Belt (Policy C12) • The site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site falls within the RAF Chalgrove aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Menlo Business Park (ASM) and Moorend Lane Farm. waste sites) • The site lies within 3km of one existing minerals site: Moorend Lane Farm. • Site lies within 3km of a nominated waste site: 274 Moorend Lane Farm. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site does not operate as an existing waste site but is in industrial use. The site lies within 2km of Thame is therefore suitable to provide non-strategic and small-scale waste management capacity in accordance with Policy W4.

The site lies adjacent to the Oxfordshire Lorry Route Network, the A329, a single carriageway subject to a 50mph speed limit restriction. The site lies to the rear of a car show room with existing access for heavy good vehicles and is not visible from the highway.

The site is considered potentially suitable for waste uses and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 279 Site Name: Land rear of Ford Dealership, Rycote Lane, Thame

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

There is no planning history for mineral or waste uses on the site. However, planning permission was granted on 12th September 2012 for the erection of an office and warehouse building by South Oxfordshire District Council (P/12/S1230/FUL). Consent was granted for a contractor’s storage yard and associated offices on land adjoining the site to the west (P/18/S3093/FUL) on the 18th January 2019.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is in industrial use (B8 and B1(a)) and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within or adjacent to the site boundary. There is a waterbody, a notable habitat, to the north of the site.

There are European protected bat species adjacent to the site and in the local area. Other protected / notable species including Badger, Brown Hare, Hedgehog and birds.

Overall impacts are considered likely to be low

Cuttle Brook Local Nature Reserve lies approximately 1.4km to east.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting.

It is a brownfield site currently used for storage along A329 just outside Thame. Site abuts A329 and is bounded by industrial units and agricultural fields

on the southern and northern boundaries respectively reducing the site’s landscape sensitivity.

The development will be viewed in the context of the adjacent industrial unit reducing any visual impact. Impact of development on local landscape character is expected to be limited.

Compliance with Policy C10: Transport - Highways Officer Assessment

The access from Christmas Lane is close to the flare of the Rycote Lane roundabout. During the peak hours, Rycote Lane and Aylesbury Road roundabouts have congestion issues.

Conclusion

The site is a previously developed site in close proximity to Thame.

It would be seen in the context of the adjoining industrial units and therefore landscape impacts would be low. The site benefits from good access to the Oxfordshire Lorry Route Network and there are no in principle reasons for restricting future waste management uses on the site that could not be overcome with appropriate mitigation.

RECOMMENDATION

It is recommended that the site is allocated for waste management uses in the Local Plan.

Site 283 – Hatford Quarry Extension, Stanford in the Vale Site Information (as nominated in 2018)

Site Location Hatford Quarry Stanford Extension, Stanford in the Vale

Grid Reference SU335942

Administrative Area Vale of White Horse

Parish Stanford in the Vale

Site Nominee(s) Hatford Quarry Ltd

Proposed Reuse/recycling for inert fill, Development soils, construction/demolition/ excavation materials Site Area 27 ha

Existing capacity N/A

Annual Throughput N/A

Existing land use Agriculture

Access Potential for direct access onto A417 Current levels and N/A types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. (Policy W4) • The site is over 5km from a large town and over 2km from a small town. • Site lies 900m from the Oxfordshire lorry network (A417). • The site is not in the AONB or within 200m from a SAC. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Site lies approximately 550m from Shellingford Crossroads Quarry SSSI. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site is within Flood Zone 1 but adjoins an area within Flood Zone 3 to the east. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies within 250m of the Hatford Conservation Area. • Site lies within 300m of Stanford in the Vale Conservation Area. • There are 6 listed buildings approximately 300m north of site in Hatford. • Numerous listed buildings over 300m away in Stanford in the Vale. • The site contains no archaeological features; as such there are no archaeological constraints to this allocation. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies 900m from A417. C10) • Nearest bus stop 700m to the east of the site in Hatford. • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies 1km from a fatal RTI on the A417 and within 3km of three serious RTIs (2 on the A417 and 1 on the B4508). Public Rights of Way (Policy C11) • Bridleway runs adjacent to western side of the site. • The Vale Way passes the site in short distance to the east. Health and Amenity (Policy C5) • The closest residential dwellings are just 250m to the east of the site and commercial properties 100m to the south.

• Dwellings in Hatford are over 300m from the site, as are dwellings in Stanford in the Vale. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of three existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale waste sites) HWRC. • Site lies within 3km of three existing minerals sites: Chinham Farm Quarry, Hatford Quarry and Shellingford Quarry. • Site lies within 3km of two nominated waste sites: 229 Shellingford Quarry and 230 Chinham Farm. • Site lies within 3km of eight nominated minerals sites: SS-03/CR-17 Hatford Quarry, South extension, SS-07/CR-24 Home Farm, SS-08/CR-16 Shellingford Quarry Western extension, SS-12/CR-12 Land at Chinham Farm (Chinham Hill), SS-15/CR-11 Hatford Quarry North extension, SS-16/CR-21 Hatford Quarry Stanford Extension and SS- 18/CR-22 Hatford Quarry West extension and SS-19/CR-23 Home Farm Carswell.

Conclusion

The site does not lie within a suitable distance to an area identified as part of Policy W4. However, the site has good access to the Oxfordshire Lorry Route Network (A417) and therefore it may be potentially be suitable for waste management uses.

The site is in close proximity to Shellingford Quarry and Chinham Farm and a number of other nominated sites and therefore cumulative impacts would need to be considered. Further consideration would also need to be given to amenity impacts given the proximity to residential properties as well as impacts on the two Conservation Areas.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 283 Site Name: Hatford Quarry Extension, Stanford in the Vale

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

There is no minerals or waste planning history on this site.

Use of this site for a waste management facility would be dependent on the site first being worked for minerals.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is currently in agricultural use. To conform with Policy W5, proposals for waste management at this site shall need to demonstrate that the site is the most suitable and sustainable option. The supporting text to Policy W5 indicates that sites in a rural location, such as this, may be appropriate for composting and biological treatment.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats or notable habitats within or adjacent to the site.

There are several (European protected) bat species within or adjacent to the site. Other protected or notable species include numerous bird, amphibian, mammal and invertebrate species.

Buckland Warren Woods Local Wildlife Site lies approximately 1km to north-east. Site partly within West Oxon Heights Streams, Hills, Woods and Parks Conservation Target Area (CTA).

Overall ecological impacts are considered likely to be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. It comprises several fields of semi-improved grassland on gently undulating topography. This together with field boundaries of low hedgerows or no planting increase inter-visibility and give a sense of openness of the landscape.

Site likely to be visible from Stanford in the Vale and Hatford settlement and conservation area.

This large allocation is expected to substantially affect the landscape character and views through the introduction of an industrial use into the open rural countryside and in close proximity to two settlements / conservation areas. Activities are also likely to substantially impact on sensitive visual receptors.

Compliance with Policy C10: Transport - Highways Officer Assessment

HGVs to be routed to avoid the local villages

There is a suitable access point from the B4508 (Fernham Road), with acceptable sightlines subject to detailed design

Conclusion

Allocation of the site for waste management uses is likely to have an adverse impact on landscape character and on sensitive visual receptors. It also has the potential to affect the Stanford in the Vale and Hatford Conservation Areas.

Given that the site requires the minerals to be extracted in the first instance, it is unlikely to make a significant contribution to waste management uses within the Local Plan period.

RECOMMENDATION

It is recommended that the site is not allocated for waste management uses in the Local Plan

Site 285 – (Magnox) Harwell Site, Harwell Campus Site Information (as nominated in 2018)

Site Location (Magnox) Harwell Site, Harwell Campus

Grid Reference SU 471 868

Administrative Area Vale of White Horse

Parish East Hendred and Harwell

Site Nominee(s) Nuclear Decommissioning Authority (NDA) and Magnox Limited

Proposed Hazardous or Radioactive Development Wastes

Site Area 85.1 hectares

Existing capacity Not known

Annual Throughput Not known

Existing land use Radioactive waste management site (former nuclear research site).

Access Existing access (within 600m of A4185)

Estimated Traffic Not known Movements

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site is an existing facility used to process radioactive waste material located at the Harwell (Policy W4 and W9) Oxford Campus and is safeguarded through Policy W9. • Site does not lie within 15km of Oxford, 5km of any large town or 2km of any small town. • The site lies approximately 1km from access onto the Oxfordshire Lorry Route Network (A34). • Site lies within the North Wessex Downs AONB. • Site does not lie within 200m of a SAC District Local Plan Allocation • Harwell Campus is allocated as a Strategic Employment Site in the Local Plan. • The land to the north of Harwell Campus (which comprises land currently subject to remediation works (known as the LETP and Sewage Farm site)) forms a proposed housing allocation in the emerging Vale of White Horse Local Plan 2031 Part 2 Submission (LPP2). This allocation was removed by the Inspector following Examination.

Biodiversity and Geodiversity • Site is just over 1km from ancient woodland (Lyde Bank Plantation). (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site lies within the North Wessex Downs AONB. Water Environment and Flooding • Site does not overlie a flood zone or source protection zone. (Policy C3 and Policy C4)) Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 6 agricultural land. Historic Environment (Policy C9) • There is a Grade II listed building within 500m east of the site. • There is a cluster of listed buildings in Chilton 1.6km south east of the site. • There are no archaeological constraints. • There are no known historic landscape constraints and no impact on historic character. Transport and Access (Policy • The site would be accessed via the Harwell Oxford Campus which direct access to Newbury C10) Road (A4185) • No serious of fatal RTIs within 3km of site. • 4 slight RTIs on M&W lorry route (A34) at junction with Newbury Road. • Bus stop within 120m of the site. • No AM peak or PM peak traffic congestion identified within proximity to site.

Public Rights of Way (Policy C11) • Public bridleway adjacent to western, northern and southern edge of site. Health and Amenity (Policy C5) • Site lies within 500m of dwellings north of the site at Alfreds Farm, 600m from residential properties north east of the site and within 1km of residential development south of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within buffer of airport safeguarding (Dalton Barracks) area. M10)

Cumulative Impact (minerals and • Site lies within 3km of one existing waste site: Prospect Farm. waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of a nominated waste site: 002 Prospect Farm. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site provides the location for an existing facility used to process radioactive wastes and is safeguarded by Policy W9. The land within the nuclear licensed site at Harwell Campus is subject to decommissioning of redundant facilities, management of waste in line with national policies and strategies for the management of waste (both directive and radioactive) and, where appropriate, the remediation of land.

The site is allocated as part of a strategic employment area at the Harwell Campus in the emerging Vale of White Horse Local Plan Part 2.

The site is accessed via the Harwell Oxford Campus which has direct access to Newbury Road (A4185) and is approximately 1km to the A34 and is within the North Wessex AONB. Development within the AONB should be refused unless it can be demonstrated that development would be in the public interest (para 172 NPPF).

Due the sites proximity to the UK Atomic Energy Authority, the strategic importance of the site and its compliance with Policy W9, the site is considered potentially suitable to provide further waste management capacity throughout the plan-period subject to no conflict arising with future employment uses proposals at the Harwell Campus.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 285 Site Name: (Magnox) Harwell Site, Harwell Campus

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The site is a former nuclear research site which is being decommissioned and consequently is currently a radioactive waste management site. There are three currently active permissions for waste management facilities as set out below:

Extension to existing waste management complex (B462) to provide a waste encapsulation and plant (WETP): outline application permitted 28.11.2003 MW.001/03; reserved matters approved 12.09.2005 MW.015/05. Application to vary condition 2, to allow for import of a small amount of Intermediate Level Waste (ILW) from Winfrith to Harwell for encapsulation and interim storage, permitted 14.09.2018 MW.0036/18. These permissions are permanent.

Waste storage facility for intermediate level radioactive waste, permitted 04.09.2017 MW.0041/17, to deal with Intermediate level waste (ILW) and Low- level waste (LLW) from Harwell and Winfrith for encapsulation and interim storage pending permanent disposal elsewhere (at the proposed national Geological Disposal Facility), for a temporary period ending 31.12.2064. (This permission varied earlier permission MW.0183/12 granted 08.07.2013.)

Installation of a semi rigid building for the temporary storage of non-radioactive waste and very low-level radioactive waste land adjacent to building 418 permitted 29.11.2018 MW.0111/18, for temporary period ending 30.11.2023.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already partly in waste management use and therefore complies with Policy W5. The site lies within the North Wessex Downs AONB. Proposals for waste uses within this site should therefore be considered against Policy C8. Major developments within the AONB will not be permitted except in exceptional circumstances and where it can be demonstrated that they are in the public interest in accordance with the NPPF.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within or adjacent to the site. The site includes notable habitats including deciduous woodland and ponds.

Records exist for European protected species namely, Great Crested Newt and several bat species. Other protected / notable species include numerous bird, amphibian, mammal and invertebrate species.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site forms part of the existing Harwell campus and is located within the AONB. It is well contained and therefore additional landscape or visual impacts are not expected. However, the site is located within the North Wessex Downs AONB which makes it more sensitive in landscape and visual terms.

The site is viewed within the context of other structures within the Harwell Campus. There are more distant views from other PRoWs on higher ground in the AONB.

Compliance with Policy C10: Transport - Highways Officer Assessment

All access roads are along private roads and therefore any upgrades to the roads will have to be done in agreement with the owners of the Harwell Campus.

Conclusion

Harwell Campus is allocated as a Strategic Employment Site in Core Policy 6 of the adopted Vale of White Horse Local Plan 2031 Part 1. Core Policy 15b (Harwell Campus Comprehensive Development Framework) of the Local Plan 2031 Part 2 ensures all new development at the Campus is guided by a comprehensive development framework, to be published as a Supplementary Planning Document. Whilst Vale of White Horse District Council note that the land identified for proposed new waste is not available for development, it is anticipated that the licensed site will be available in the longer term.

The health of existing and future residents and employees of the Campus must be considered, in accordance with paragraph 205 (b) of the National Planning Policy Framework.

The site is located within the North Wessex Downs AONB and therefore the scale and extent of development should be limited.

Policy W9 of the adopted Oxfordshire Minerals and Waste Core Strategy states that the Minerals and Waste Local Plan Part 2 - Site Allocations Document will allocate sites to make specific provision for the treatment and storage of radioactive waste.

Part of the nominated site is listed in Appendix 2 of the adopted Core Strategy as an existing and permitted waste management site safeguarded under Policy W11.

RECOMMENDATION

Parts of the site already have planning permission for waste management uses which should continue to be safeguarded in the Local Plan. The remainder of the site is not currently available for development and given its location in the AONB, would only be suitable for small scale non-strategic facilities. It is therefore recommended that the wider site is not allocated in the Local Plan Part 2 – Sites Allocations Document.

Site 287 – Ardley Fields Site Information (as nominated in 2019)

Site Location Ardley Fields

Grid Reference SP543255

Administrative Area Cherwell

Parish Ardley

Site Nominee(s) Viridor Waste Management Ltd Proposed Non-hazardous waste Development Site Area 8.9 ha

Existing capacity 324,600 tpa on wider site

Annual Throughput 291,000 tpa (2017) on wider site

Existing land use Energy recovery facility for non-hazardous waste (temporary permission until 2049) on adjacent site. Landfilling has ceased (to be restored by 2020). Access Existing access onto B430

Current levels and Unknown types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The southern site is within 15km of Oxford. Both parts of the site are within 5km of a large town (Policy W4) (Bicester). • The site has direct access onto the B430 on the Oxfordshire lorry route network. • The site is not located within an AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • Site does not conflict with a District Local Plan allocation and District Council have no in principle objections at this stage Biodiversity and Geodiversity • Site lies adjacent to the Ardley Trackways SSSI. Ardley Cutting and Quarry SSSI lies within (Policy C7) 500m north of the site. • Site overlies the Ardley Fields Quarry Local Geological Site. • A proposed Local Wildlife Site (Ardley Fields Quarry) lies 560m north of the northern site. • Site lies within 1km of Ancient Woodland (Digging Copse to the north east of the site). • Site lies within 3.5km of a Local Nature Reserve, to the southeast of the site. • Site lies in excess of 5km from International/European designated sites. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site is not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Site overlies a principal aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Grade II listed barn within 700m northwest of site. • Grade II listed building within 1.1km to the southeast (Trow Pool Water Tower). • Grade II listed Park and Garden (Middleton Park) within 1.5km to the south. • Site does not lie in close proximity to a conservation area.

• This allocation site is a former quarry and any archaeological features will have been removed. As such there are no archaeological constraints to this allocation site. • No impact on historic character expected.

Transport and Access (Policy • Site lies within 2.5km of the A43. C10) • Nearest bus stop is within 2km south of the site. • AM peak or PM peak traffic congestion identified within proximity to site. • There are no ‘serious’ RTI histories within 3km of the site. • Site is an existing landfill, HWRC and ERF site – no works required to improve access. Public Rights of Way (Policy C11) • Public bridleway crosses the western site and runs along the eastern boundary of the eastern site Health and Amenity (Policy C5) • Residential dwellings located within 300m west of the site. Green Belt (Policy C12) • Site is not located within the Green Belt. Aerodrome Safeguarding (Policy • Site located within the London Oxford Airport aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of an existing waste site: Ashgrove Farm waste sites) • Site lies within 3km of an existing minerals site: Dewars Farm Quarry. • Site lies within 3km of one nominated waste site: 226 Dewars Farm Quarry. • Site lies within 3km of two nominated minerals sites: CR-13 Dewars Farm Quarry East extension and CR-19 Dewars Farm Quarry south extension.

Conclusion

Key considerations in further promoting the site for waste management uses are the underlying water bodies and the potential impact on nearby environmental designations, particularly since the site lies in close proximity to a number of other existing minerals and waste operations.

However due to the proximity to the Ardley ERF, there may be potential to provide complimentary material processing activities within the site.

The site should therefore be subject to further detailed assessment in determining its potential to provide further waste management activities on site.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 287 Site Name: Ardley Fields

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The site is part of a wider existing operational waste management site comprising a landfill site, energy recovery facility and household waste recycling centre.

The current primary planning permission for the landfill site and energy recovery facility was approved under a s73 application (MW.0085/17, granted 22nd June 2018) which allows continuation of the development permitted by MW.0044/08 (the construction and operation of an energy from waste and combined heat and power facility and the continuation of landfill operations and landfill gas utilisation.

This permission restricts the input of waste to the site, as follows: No more than 500,000t of waste per annum shall be imported to the site until the completion of landfilling at the site, after which no more than 326,300t of waste per annum shall be imported to the site for treatment at the ERF.

Landfilling is required to cease by 31st December 2019 and restoration of the landfill site is required to be completed by 31st December 2020.

The existing Household Waste Recycling Centre is permitted to be retained under permission MW.0103/17 granted 19th October 2018; it is required to be removed by 31st December 2026 and the site restored within 12 months.

Under permission MW.0085/17, the landfill was to be completed by 2019 and site restored by 2020. Landfilling of waste at the site has now ceased and the site only receives soils/sub-soils for the restoration of the landfill.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within the site. Irreplaceable habitats adjacent to the site include several ancient woodlands within 1km.

In terms of notable habitats, there are ponds within/adjacent to the site.

European protected species within or adjacent to the site include Great Crested Newt and several bat species. Other protected/notable species include numerous bird, amphibian, mammal and invertebrate species.

There are several Local Wildlife Sites, the closest being the Trow Pool LWS approximately 350m to the south-east of the site Tusmore & Shellswell Park Conservation Target Area (CTA) lies approximately1.4km to north-east.

The site is currently disturbed however it is to be restored.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It forms part of a larger complex of mineral extraction, landfill and waste processing sites and proposed activity would be viewed in this context, reducing the visual sensitivity. Noise and smell affect perception of local character.

Proposal affects existing quarry and landfill site that is currently being restored to reflect landscape character and ecological enhancements.

Overall the landscape and visual impact of the proposal are likely to be low, but care will have to be taken that proposed new use does not compromise landscape benefits to be delivered by the current restoration.

Compliance with Policy C10: Transport - Highways Officer Assessment

Site would use existing access to B430 (Freight Priority Network - Tertiary) which includes right turn filter lane. The existing access has good visibility with gates set well back.

There is a routeing agreement in place for all HGVs other than RCVs serving the route through Middleton Stoney. There are already high volumes of traffic through Ardley and Middleton Stoney.

The B430 is getting busier with Heyford Park development; it is also used as a rat-run to avoid M40 junction 9.

Conclusion

The site is part of a wider existing operational waste management site comprising a landfill site, energy recovery facility and household waste recycling centre. The nominated areas are adjacent to the ERF plant site and do not conflict with that operation. Landfilling of waste has now ceased and the landfill is in the process of restoration.

There are no in principle reasons why the site should not continue to operate for waste management uses, particularly given the proximity to the Ardley ERF and the potential to provide complimentary material processing activities within the site.

RECOMMENDATION

It is recommended that the site is allocated in the Local Plan for waste management uses.

Site 289 – Overthorpe Industrial Estate, Banbury Site Information (as nominated in 2018)

Site Location Overthorpe Industrial Estate, Banbury

Grid Reference SP 468 402

Administrative Area Cherwell

Parish Banbury Site Nominee(s) Grundon Waste Management Limited Proposed Retention of transfer station Development and recycling centre and potential for further waste recycling and recovery operations. Site Area 2.78 ha

Existing capacity 145,000 tpa

Annual Throughput 2017: 55,000 tpa 2016: 55,600 tpa 2015: 45,500 tpa Existing land use Transfer station and recycling centre for non-hazardous waste and adjacent undeveloped land. Access Existing access onto Thorpe Way (within 1.5km of A422 and M40) Current levels and 110 HGV movements (55 in types of traffic and 55 out) daily movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • Part of the site currently operates as an existing transfer station and recycling centre and is (Policy W4) located within the Overthorpe Industrial Estate in Banbury. The remaining, larger part of the site is currently undeveloped. • The site lies within 5km of Banbury. • The site has good access to the Oxfordshire Lorry Route network (approximately 1.3km from the A4260 and approximately 2km from the A422 access to the M40). • The site is not located in an AONB. • The site is not within a 200m buffer of a Special Area of Conservation. District Local Plan Allocation • Site partially overlies Strategic Employment site allocated within the Local Plan, Banbury 6 – Employment Land West of M40. • The site nomination shows the access road to the site through land allocated in the Local Plan as existing green space (allotments). Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site lies within Flood Zones 2 and 3. • Area in Flood Zone 3 benefits from flood defences. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site lies 1.3km from the nearest AQMA (Banbury town centre). Soil Resources (Policy C6) • Site within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • Site lies within 500m of Grimsbury Conservation area. • Site lies within 700m of a Scheduled Monument (Former World War I National Filling Factory). • There are Listed buildings within 800m west of the site on the outskirts of Banbury. • The site has been extensively disturbed by previous development. No known archaeological constraints. Transport and Access (Policy • Access to Overthorpe Industrial Estate is via Overthrope Road, Thorpe Way and Thorpe C10) Mead. • Bus stop within 500m north of site.

• Area of AM and PM peak traffic congestion identified within proximity to site. • Site lies in close proximity to an area with history of RTIs (6 ‘serious’ RTI histories within 3km of the site). Public Rights of Way (Policy C11) • No public rights of way are in the vicinity of the site. Health and Amenity (Policy C5) • Site lies in close proximity to residential properties in Banbury (less than 100m). Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • The site is on in an existing industrial estate. It lies within 3km of three waste sites: Thorpe Mead 2a/3a; Banbury waste sites) STW; and Thorpe Lane Depot. • Merton Street Depot (Grundon); Allotment Land, Thorpe Mead; Thorpe Mead 2a/3a; Banbury Transfer Station; Banbury Strategic STW; and Thorpe Lane Depot. • There are no existing minerals sites within 3km of the site. • Site lies within 3km of a nominated waste site: 232 Banbury STW. • There are no nominated minerals sites within 3km of the site.

Conclusion

Part of the site is an existing strategic waste management facility located on an industrial estate in Banbury. The site lies therefore lies within 5km of Banbury and would be suitable to provide either a strategic, non-strategic or small-scale waste management capacity in accordance with Policy W4.

The site may be suitable for some expansion, but regard must be had to the close proximity of residential development and public open space (allotments).

The site is considered potentially suitable for waste uses and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 289 Site Name: Overthorpe Industrial Estate

Stage 1b: Detailed Assessment

PLANNING HISTORY

Part of the site is currently a permanent waste transfer station (CHN.352/93 granted in 1994) with an annual throughput of around 45-55,000tpa.

Permission to construct a new, permanent materials recovery facility (MRF) including storage, workshops and vehicle parking on greenfield land adjacent to existing waste transfer station, including retention and extension of the existing waste transfer station was granted on 15.02.2011 (MW.015/06). Permission was granted on 12.02 2014 (MW.0149/13) to amend the conditions on the MRF consent to allow it to be implemented in two phases: Phase 1 new haul road and site access; Phase 2 all other development. A further variation to the permission was granted 01.12.2017 (MW.0056/17) for changes to phasing and design.

The permission issued in 2011 was subject to a Section 106 agreement which requires that once the new MRF is built and fully operational, Grundon’s must cease waste management operations at their nearby Merton Street site within three years of implementation of the permission of the MRF.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

Part of the site is already in existing waste management use. The remainder of the site has an extant consent for a Materials Recovery Facility. The principle use of the site for waste management uses therefore complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known irreplaceable or notable habitats within or adjacent to the site.

There are records of several bat species, a European protected species, within or adjacent to site. Other protected and notable species include several bird, amphibian, mammal and invertebrate species.

The site is unlikely to pose any ecological constraints.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is partially developed for waste management uses set within the context of an industrial estate. Allotment gardens adjoin the undeveloped part of the site to the north west. Aerial photography suggests that the development land to the rear of the existing waste transfer centre was formerly also used for allotments. There may be a potential impact on the amenity of the allotments and the adjacent open space.

There would be potential views from the allotments, adjacent open space, nearby residential properties, the industrial estate and from trains which run along the railway line to the south of the site.

There are currently no known historic landscape constraints.

Overall the landscape and visual impact of the proposal is considered to be low in the light of existing use and context of the site.

Compliance with Policy C10: Transport - Highways Officer Assessment

There is direct access to Thorpe Way via Overthorpe Road through the Thorpe Way industrial estate. Access to the freight route (M40) does however get congested at peak times. There would however be no objection in principle to using the route.

A new temporary site access on to Thorpe Way in association with the haul road (Phase 1) of the works for the MRF (MW.0149/13) has already been implemented. Under the extant consent the approved site access works onto Thorpe Way must be fully completed prior to any development in Phase 2 taking place. There is therefore no highway objection in principle to waste development on this site.

A short section of road from Thorpe Way serves both the proposed site and the allotments. However the access to the Grundon site is then separate to the access to the allotments.

Conclusion

This site already has the benefit of an extant consent for waste management uses.

The waste transfer centre operated by Grundon is an existing, permanent waste management facility. Core Strategy Policy W7 already safeguards such operational waste management sites and the allocation of the site in the Local Plan is not going to make a significant contribution to meeting waste management needs. It is not therefore recommended that this part of the site is allocated in the Local Plan.

The remainder of the site has consent for a MRF which has yet to be implemented although some preparatory works have been carried out at the site access to Thorpe Way. On this basis, the site is considered suitable for allocation in the Sites Local Plan as there is no objection in principle to waste management uses on this site.

RECOMMENDATION

Part of the site not currently use but with extant consent for waste management purposes for is suitable for allocation in the sites plan.

Site 290 – Culham Science Centre Site Information (as nominated in 2018)

Site Location Culham Science Centre, Abingdon

Grid Reference SU534958

Administrative Area South Oxfordshire

Parish Clifton Hampden

Site Nominee(s) UKAEA

Proposed Management of onsite waste Development (small quantities of controlled (inc Haz.) radioactive waste materials in solid or liquid forms) from fusion research activities. Site Area Unknown Existing capacity <100 tpa

Annual Throughput Unknown Existing land use Facility for the processing of radioactive materials and controlled waste from adjacent atomic industries. Access Existing access onto Abingdon Road (A415) Current levels and Unknown types of traffic movement

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Waste Strategy • The site lies within 5km of Abingdon and 15km of Oxford. (Policy W4 and W9) • The site lies within 1.5km from access onto the Oxfordshire Lorry Route Network (A415) to the south of the site. • Site does not lie within 200m of a SAC • Site does not lie within AONB. District Local Plan Allocation • This site is not allocated in the District Local Plan. Biodiversity and Geodiversity • Little Wittenham SAC is approximately 3.7km south-east (Policy C7) Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site is not within 1km of a Local Wildlife Site. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is located within 3km of an AONB. Water Environment and Flooding • Site not within a flood zone or source protection zone. (Policy C3 and Policy C4)) • Proposal not water compatible. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • The site is not classified as agricultural land. Historic Environment (Policy C9) • Site within 700m of a Grade II listed building to the west (Thame Lane Bridge) and two Grade II listed buildings in Clifton Hampden (Courtiers and Garden Wall approximately 10 metres south east of Courtiers). Also within 710m of a Grade II listed building to the south (Fullamoor Farmhouse), • Site does not lie within 500m of any Scheduled Monuments. • Site lies within 600m of Clifton Hampden Conservation Area.

• There are currently no known archaeological constraints. Transport and Access (Policy • Site has access to the A415 via Culham Science Centre. C10) • Site is not adjacent to a bus stop. • Culham train station lies within 800m of the site. • This site may impact on both AM and PM congestion on the A415. • There is no RTI history within 3km of the site. • Existing facility for the processing of radioactive materials and controlled waste. Unlikely works will be required to improve access. Public Rights of Way (Policy C11) • No PROW within or adjacent to the site. Health and Amenity (Policy C5) • Residential dwellings lie approximately 750m to the east of the site within Clifton Hampden. Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Dalton Barracks, RAF Chalgrove, and RAF Benson aerodrome M10) safeguarding areas.

Cumulative Impact (minerals and • Site lies within 3km of three existing waste sites: Sutton Courtenay, Hill Farm and Berinsfield Car Breakers. waste sites) • Site lies within 3km of an existing minerals site: Sutton Courtenay Quarry (Bridge Farm). • Site lies within 3km of three nominated waste sites: 010 Sutton Courtenay Landfill, 217 Culham No.4 Site and 248 Thrupp Lane, Radley. • Site lies within 3km of five nominated minerals sites: SG-17 Land at Culham, SG-41 North of Lower Radley, SG-42 Nuneham Courtenay, SG-62 Appleford and PFA-01 Land at Thrupp Lane, Radley.

Conclusion

The site provides the location for an existing facility used to process radioactive and controlled wastes.

The site lies close to the Oxfordshire Lorry Route Network (A415) to the south of the site. Access to this route is through the Culham Science Centre complex, the complex itself lies within 200m to the route.

The site is an existing developed waste facility within the Green Belt. Development within the Green Belt would be inappropriate unless it would involve the replacement of a building, providing the new building is in the same use and not materially larger than the one it replaces; or is for the partially or complete redevelopment of previously development land provide it would not have a greater impact on the openness of the Green Bet than the existing development (NPPF 145).

Due the site’s proximity to the UK Atomic Energy Authority and proximity to the Oxfordshire Lorry Route Network, the site is considered potentially suitable to provide further waste management capacity throughout the plan-period.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Site No: 290 Site Name: Culham Science Centre

Stage 1b: Detailed Assessment

PLANNING HISTORY

The United Kingdom Atomic Energy Authority (UKAEA) hosts and operates the Joint European Torus (JET) project at Culham Science Centre. The JET project buildings at Culham Science Centre were originally permitted under temporary consents in the 1970s. However, the majority of the JET project buildings were granted by South Oxfordshire District Council in 2014. Planning permission was granted for the permanent Materials Detritiation Facility for the processing of radioactive materials on 20.04.2016 (MW.0034/16).

Some buildings associated with JET will be retained when the project ceases, but others are subject to temporary permission. An extension of the ground and first floor to building J30, an existing radioactive waste handling facility, was permitted 04.03.2015 (MW.0155/14), for temporary period ending 31.12.2030. A RUBB tent and modified ISO container for packaging of approx. 30 tonnes of radioactive waste per year, for off-site transportation, within the J30 compound was permitted on 6.02.2015 (MW.0156/14), again for a temporary period ending 31.12.2030. Some radioactive waste will result when decommissioning of these sites takes places.

ASSESSMENT

Compliance with Policy W5: Siting of Waste Management Facilities

The site is already in waste management use and therefore in principle the site complies with Policy W5.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment There are no known records of irreplaceable habitats within or adjacent to the site. Notable habitats include small areas of woodland and waterbodies close to the site boundary.

Records of European protected species in the vicinity include Great Crested Newt and several bat species. Other protected and notable species include records of numerous bird, amphibian, mammal and invertebrate species.

Furze Brake LWS is to north of site and two Conservation Target Areas within 1km (the Thames Clifton to Shillingford and Thames Radley to Abingdon).

Culham Science Centre is however a large site and so land within and adjacent to it is already experiencing existing disturbance.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is well contained and within the Science Centre that is clearly defined by a perimeter fence. The landscape context comprises the wider business park and a sewage works and which reduces the sensitivity of the immediate landscape character to the site. Landscape character sensitivity does however increase towards the north (Nuneham Park) and east (Clifton Hampden Area); both conservation areas which are a short distance away.

The site can be viewed through the security fence from a public right of way that runs along the northern periphery of the site and from Abingdon Road.

There are currently no known historic landscape constraints.

The overall landscape and visual impact of further waste management uses on this site is expected to remain low.

Compliance with Policy C10: Transport - Highways Officer Assessment

No known highway constraints.

Conclusion

UKAEA has a strategic plan in place that has been published as “Site Development Guidance vrs 2”, that aligns with the local plan and indicates how the Science Centre at Culham is being envisaged to develop. The site has planning permission for a permanent Materials Detritiation Facility for the processing of radioactive materials and other temporary consents for related uses.

The site is however located in the Green Belt. Paragraph 144 of the NPPF advises that substantial weight should be given to any harm to the Green Belt. ‘Very special circumstances’ will not exist unless the potential harm to the Green Belt by reason of inappropriateness, and any other harm resulting from the proposal, is clearly outweighed by other considerations (Policy C12 of the Core Strategy).

This site nomination is not for the “specific provision” for any the 3 specified types of radioactive waste management listed in the second part of Policy W9 of the Core Strategy additional to what is already permitted. There is therefore no justification for allocating this site, particularly given its location in Green

Belt.

The site is however previously developed and forms of the Culham Science Centre. Any development proposals can therefore be considered under the first part of Policy W9 which indicates that in principle such development may be acceptable. It is not therefore considered necessary to make a specific site allocation within the Local Plan.

RECOMMENDATION

The site does need to be allocated in the Site Plan.

Site CR-07: Adjacent to Whitehill Quarry

Site Information (as nominated in 2018) Site Location Adjacent to Whitehill Quarry

Grid Reference SP269102

Administrative Area West Oxfordshire

Parish Shilton Site Nominee(s) DD Farms Proposed Development Crushed rock extraction. Potential new quarry or extension to Whitehill Quarry. Site Area 26.12 ha Estimated annual Unknown output Estimated Reserves Estimated total yield of 5 mts. (including depth/ Depth and overburden and working depth unknown. overburden) Proposed Restoration Unknown Access Existing access onto A40 (Smith+Sons Whitehill Quarry entrance – subject to agreement) Estimated Unknown Traffic Movements Year of ASAP subject to planning. Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Area for crushed rock (Burford – South of A40). Strategy – Strategic Resource • Site lies within the northern part of the County (West Oxfordshire). Areas (Policy M3) • Site is proposed as a possible extension to the Whitehill Quarry. • Estimated total yield is 5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site adjoins the Whitehill Quarry Local Geological Site to the north. (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 3km from SSSI, NNR, SINC or LNR. • Site is within 1km of a Priority Habitat Creation Area at the River Windrush at Widford. Landscape / Visual (Policy C8) • Site lies within 500m of the Cotswolds AONB. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a Principal and Secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There is a listed building approximately 780m to the north of the site off White Hill; and a second approximately 400m to the east at Stonelands. • No known archaeological constraints on designated or non-designated assets heritage assets • Site is located immediately north west of Akeman Street, a Roman Road from Cirencester to St Albans. There is some evidence of activity adjacent to Akeman Street in the form of farmsteads or small roadside settlements. In the vicinity of the proposed site there is evidence of cemeteries that presumably are associated with settlement sites. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site is approximately 450m south of the Oxfordshire Lorry Route Network (A40) and would use C10) existing site access to Whitehill Quarry. • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies within 2km of an area identified with history of a fatal RTI. Public Rights of Way (Policy C11) • There is a bridleway which runs through the centre of the site connecting Widford, north of the site, with the B4020 to the south. The bridleway through the existing Whitehilll Quarry is subject to a diversion order expiring in 2023 at the latest.

© Adams Hendry Consulting Ltd. 339 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • Stone Lea Farm is adjacent to the site to the east. A number of properties and businesses are located at Sturt Farm approximately 270m north east of the site. • The Blue Cross rehoming centre, Burford is approximately 150m to the south west of the site. • Burford is approximately 1.5 km away to the north west. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Claridges Car Breakers, Worsham,Quarry and Shipton Hill. (minerals and waste sites) • Site lies within 3km of 2 existing minerals sites: Burford Quarry and Whitehill Quarry. • Site lies within 3km of 1 nominated waste site: 026 Whitehill Quarry. • Site lies within 3km of 1 nominated minerals site: CR-10 Burford Quarry SW Extension.

Conclusion

The site is nominated as an extension to Whitehill Quarry and lies within the Mineral Strategic Resource Area (Burford – South of A40).

Due to its links with an existing mineral site, the site has direct access onto the Oxfordshire Lorry Route Network (A40), with onward access to London, South Wales and the West.

The site lies within 500m of the Cotswolds AONB and potential impacts on this designation will be a key consideration in promoting this site for mineral development. A further consideration is the underlying groundwater, since the site overlies both Principal and Secondary aquifers; and the potential impacts on the health and amenity of nearby residential and commercial properties.

Based on the outcome of this initial site assessment, the site nominated site is considered to have potential for mineral development and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no minerals or waste planning history on the nominated site itself.

The adjoins and is proposed as an extension to the existing Whitehill Quarry.

Whitehill Quarry has permission for quarrying and construction of a new access under 3 determinations of new conditions under IDO and ROMP procedures: MW.006/04, permitted 02.07.2004; MW.007/04, permitted 02.07.2004; MW.008/04, permitted 02.07.2004. Conditions require mineral extraction to cease by 21.02.2042, and the site to be restored by 21.02.2043.

The new access has been constructed and some working has been taken place in recent years but the quarry is currently inactive as the operator is working the nearby Burford Quarry.

Final restoration scheme, including phasing, aftercare and a revised timetable for the drystone walling is outstanding.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records show significant deposits of white limestone and forest marble overlaid by a limited extent of overburden. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known irreplaceable habitats or notable habitats within or adjacent to the site.

There are recordings of several different European protected species of bat within the local area as well as recordings for several protected and notable mammal, bird, amphibian, plant and invertebrate species.

© Adams Hendry Consulting Ltd. 341 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 The site lies approximately 680m from the South Cotswolds Valleys Conservation Target Area and 850m from the Upper Windrush Conservation Target Area.

The site or the adjacent areas will achieve a net gain in restoration and enhancement of biodiversity, in line with the objectives of the respective Conservation Target Areas. As the extent of this is as of yet unknown, the details have not been confirmed.

Overall the ecological impacts of the proposals are likely to be low, however must be informed by ecological assessment. No significant impacts on any statutory site of nature conservation interest are anticipated. Biodiversity net gain to be achieved on site or adjacent and restoration/enhancement shall be in line with the objectives of the CTA.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is approximately 400m from the boundary of the Cotswold AONB, increasing the site’s landscape and visual sensitivity.

Noise, activity and lorry movements have the potential to impact on the perception of the AONB, however views from the AONB are likely to be limited to the A40 due to the sloping topography.

The landscape context is of large open intensive agricultural fields with hedgerows. Boundary vegetation predominantly low giving a sense of openness. Extraction would be partly viewed in the context of existing White Hill quarry and Westerfield solar farm, which act as visual detractors.

Bridleway crosses the site in north-southerly direction and will need to be diverted. A footpath runs a short distance north of the site and through the existing quarry.

Development is unlikely to be visible from PRoWs in the AONB but occasional views from A40 (AONB boundary) exist.

Eastern boundary of proposed site aligns is old Roman Road (Akeman Street) – impact would need to be avoided. Extraction is likely to moderately impact on the historic character. Potentially historic boundary features need to be retained.

Overall this proposed extension is considered to moderately affect the local landscape character and views.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

No impact on local lorry route as access would be through existing Whitehill quarry directly on to the A40 (Freight Priority Network - Primary). There is a right turn filter lane from A40

No local traffic impact, although A361 roundabout (1 mile west of site) can be congested at times.

Conclusion

The site lies within the Mineral Strategic Resource Area (Burford area south of A40) and has been nominated as an extension to Whitehill quarry. It has direct access onto the Oxfordshire Lorry Route Network (A40) and is likely to have limited impact on the local highway network.

The ecological impacts are likely to be low and there are no known archaeological constraints. Mineral extraction is likely to moderately affect landscape character, which is more sensitive given the proximity to the Cotswolds AONB.

There are a number of existing and nominated mineral and waste sites within 3km of the site and therefore cumulative impacts will need to be considered taking into account the overall requirement for crushed rock over the plan period set out in the Core Strategy.

Site CR-10: Burford Quarry SW Extension

Site Information (as nominated in 2018) Site Location Burford Quarry SW Extension Grid Reference SP273 092 Administrative Area West Oxfordshire Parish Shilton Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Development Crushed rock extraction. Potential extension to Burford Quarry. Site Area 12.4 ha Estimated annual Up to 200,000 tpa output Estimated Reserves Estimated total yield of 1.6 mts. (including depth/ Estimated working depth is 7.0-8.0m below ground surface. overburden) Overburden estimated at 2.0-2.5m. Proposed Restoration Progressive restoration to a mix of agricultural land, calcareous grassland, woodland and with enhanced biodiversity and opportunities for geodiversity with access to rock faces. Access Existing quarry access onto the Burford Road and north to the A40 with existing routing agreement. Estimated 58 HGV movements per day. Traffic Movements Year of No later than 2035. Commencement Lifetime of Current reserves have a duration of 20 Operation years. End date for extraction 2037.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • The northern part of the site (approximately 70%) is located within the Mineral Strategic Strategy – Strategic Resource Resource Area for crushed rock (Burford – South of A40) Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • Site is proposed as a possible extension to the Burford Quarry. • Estimated total yield is 1.6 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • Land to the east of Swinbrook Road, Caterton (approximately 500m at its closest point from the nominated site) is allocated in the West Oxfordshire Local Plan for approximately 70 dwellings. Biodiversity and Geodiversity • Site adjoins the Burford Quarry Local Geological Site to the north and east (Policy C7) • Site located in excess of 5km from International / European designated sites. • Site not within or adjacent to ancient woodland. • Site located in excess of 3km from SSSI, NNR, SINC or LNR. Landscape / Visual (Policy C8) • The Cotswolds AONB lies 1.1km to the north of the Site. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a Principal aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • The Shilton conservation area lies 400m to the south west of the site. • There are numerous listed buildings within Shilton, the closest of which is approximately 400m to the south west of the site. • There are currently no known historic landscape constraints Transport and Access (Policy • Site is approximately 1.2km from the Oxfordshire Lorry route Network (A40) assuming the C10) existing site access to Burford Quarry can be used. • The site lies in close proximity to an area with a history of RTI’s. • No AM peak or PM peak traffic congestion areas identified within close proximity to site. Public Rights of Way (Policy C11) • There is a public right of way running north/south approximately 300m to the east of the site and another one running east-west approximately 250m to the south of the site. Health and Amenity (Policy C5) • The nearest residential receptor is 350m to the south west of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt.

© Adams Hendry Consulting Ltd. 346 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Claridges Car Breakers, and Worsham Quarry. (minerals and waste sites) • Site lies within 3km of 2 existing minerals sites: Burford Quarry and Whitehill Quarry. • Site lies within 3km of 1 nominated waste site: Whitehill Quarry. • Site lies within 3km of 1 nominated minerals site: CR-07 Adjacent to Whitehill Quarry.

Conclusion

The site has been nominated as an extension to the existing Burford Quarry and is largely within the Mineral Strategic Resource Area for crushed rock. The site has potential to use the existing access route associated with the existing quarry site on to Burford Road, which further provides access onto the Oxfordshire Lorry Route Network (A40) approximately 1.2km to the north of the site access.

There is potential to develop the site for mineral extraction and it will therefore be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

The nominated site would be an extension to the existing permitted and operational Burford Quarry, which also has a blockworks within the quarry site.

The currently active planning permission for Burford Quarry is MW.0032/18, permitted 28.05.2019: Section 73 application to continue the development permitted by planning permission 15/04243/CM (continuation of development without complying with condition 45 (Surface Water Management Scheme) of planning permission 14/0725/P/CM for the development of integrated working and restoration for limestone extraction for producing aggregates and reconstituted stone products, in order to enable amendments to the Surface Water Management Scheme) without complying with conditions 1, 3, 4, 6 and 16 in order to extend the timescale for limestone working to 2035 with restoration by 2036, amend the phasing and restoration proposals and to amend legal agreements to allow the importation of limestone from Whitehill Quarry and to allow the blockworks to operate until 2035. Conditions require: • Cessation of mineral working and deposit of mineral waste by 31.12.2035; • Restoration of site by 31.12.2036; • No more than 200,000 tonnes to be extracted in any calendar year.

This application stated that at the beginning of 2017 there were approximately 2.0 mt of permitted reserves of limestone remaining to be worked from the site; that the historic rate of working has been 100,000 tpa; that working is expected to continue at an average rate of 100,000 tpa; and that the remaining reserves are expected to be worked by the end of 2035

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Limited borehole records available to assess quality. However, borehole records taken approximately 500m to the south of the site indicate the presence of oolitic limestone at 1.5m bgl. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

A small woodland area adjacent to the north-east is considered a notable habitat, but no irreplaceable habitats have been identified within or adjacent to the site.

Several bat species protected under European legislation have been recorded in the local area together with other protected and notable species including mammals, birds, amphibians, plants and invertebrates.

© Adams Hendry Consulting Ltd. 348 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Carterton Grasslands Local Wildlife Site is situated approximately 1.5km to the south, and South Cotswolds Valley Conservation Target Area (CTA) approximately 340m from the site.

The site appears to be a single arable field located adjacent to an existing quarry. Overall biodiversity and geodiversity impacts are likely be low.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is approximately 1.1km from the boundary of the Cotswold AONB. It would not be visible from the AONB and impacts are likely to be limited to lorry movements.

It is proposed as a new large extension to existing quarry, which will result in the loss of large open arable field. The nearby quarry and loss of characteristic hedgerows and boundary vegetation reduce landscape sensitivity. Landscape impact partly depends on the phasing and restoration of the existing quarry. Restoration offers opportunities for enhancing landscape character in the long term.

The lack of PRoWs within the immediate vicinity of the site reduces the visual sensitivity of the site but views from adjacent lane and more distant PRoWs and Shilton will be affected.

Overall the landscape and visual impact of the proposed extension is considered to be moderate.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment There is an existing route agreement providing access to the A40 (Freight Priority Network - Primary)

Existing access has good visibility with gates set well back.

Conclusion

The site lies partially within the Mineral Strategic Resource Area and is proposed as an extension to Burford Quarry, which has consent for mineral extraction until the end of 2035. It has access to the Oxfordshire lorry route network (A40). Biodiversity impacts are considered to be low and landscape and visual impacts moderate.

The adopted West Oxfordshire Local Plan allocates land approximately 500m to the south east of the site for residential development and therefore any potential extension to Burford quarry should take into account potential future residential amenity impacts so as not to compromise the implementation of this allocation.

There are a number of existing and nominated mineral and waste sites within 3km of the site and therefore cumulative impacts will need to be considered

© Adams Hendry Consulting Ltd. 349 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 taking into account the overall requirement for crushed rock over the plan period set out in the Core Strategy.

Site CR-13: Dewars Farm Quarry East Extension

Site Information (as nominated in 2018) Site Location Dewars Farm Quarry East Extension Grid Reference SP547254 Administrative Area Cherwell Parish Bucknell Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Development Crushed rock extraction. Potential extension to Dewars Farm Quarry. Site Area 35 ha Estimated annual 250,000 tpa output Estimated Reserves Estimates yield of 3.6 mts (including depth/ Estimated working depth of 5-10m Estimated overburden of 1.25m overburden) Proposed Restoration Low level agricultural use with biodiversity enhancements including open water ponds on the low ground adjacent to the Gagle Brook with marginal habitats managed for wildlife. Access Existing purpose built Dewars Farm Quarry access on to the B430. Estimated c. 95 lorry movements (in and out) Traffic per day. Movements Year of 2025 before exhaustion of existing Commencement consented reserves in 2027. Lifetime of 9-10 years. End date for extraction Operation 2027.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Area (North West Bicester) Strategy – Strategic Resource • Site lies within the northern part of the County (Cherwell). Areas (Policy M3) • Site is proposed as a potential extension to Dewars Farm Quarry. • Estimated site yield is 3.6 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies adjacent to the Ardley Cutting and Quarry SSSI to the north and the Ardley Trackways (Policy C7) SSSI to the south. • Site lies adjacent to the Ardley Fields Quarry Local Geological Site. • Site lies adjacent to a proposed Local Wildlife Site (Ardley Fields Quarry). • Site lies within 500m of Ancient Woodland (Digging Copse) to the north east. • Site lies within 3km of a Local Nature Reserve. • Site lies in excess of 5km from International/European designated sites. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site is not within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a principal aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 3 agricultural land. • Restoration proposed. Historic Environment (Policy C9) • Grade II listed building within 200m to the east (Trow Pool Water Tower). • Grade II listed Park and Garden (Middleton Park) within 2km to the south. • Site does not lie in close proximity to a conservation area. • The site is located in an area of considerable archaeological interest. Archaeological investigations for the current extraction area at Dewars Farm have revealed extensive evidence of later prehistoric activity including a settlement area and a pit alignment along with an Anglo-Saxon cemetery. • There are currently no known historic landscape constraints. Transport and Access (Policy • The site lies adjacent to the Oxfordshire Lorry Route Network (B430) a local access road. C10) • The M40 is with 3km of the site and adjoins its eastern boundary • Access would be via the existing access at Dewars Farm Quarry. • AM peak or PM peak traffic congestion areas identified within proximity to site.

© Adams Hendry Consulting Ltd. 353 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Public Rights of Way (Policy C11) • Public bridleway adjacent to western and northern boundary of site. • Public footpath adjacent to south eastern boundary of site. • Restoration proposed. Health and Amenity (Policy C5) • The site is adjacent to the Virdor ERF and approximately 1km east of Severn Trent Green Power at Ardley. • Residential properties are located approximately 780m north west of the site. • Green Belt (Policy C12) • Site is not located within the Green Belt. Aerodrome Safeguarding (Policy • Site located within the London Oxford Airport aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Ashgrove Farm and Ardley Landfill / ERF / HWRC. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Dewars Farm Quarry. • Site lies within 3km of 2 nominated waste sites: 226 Dewars Farm Quarry and 287 Ardley Fields. • Site lies within 3km of 1 nominated minerals site: CR-19 Dewars Farm Quarry South Extension.

Conclusion

The site is nominated as a proposed extension to Dewars Farm Quarry and lies within the Mineral Strategic Resource Area (North West Bicester). The site has potential to access directly onto the Oxfordshire Lorry Route Network (B430) via the existing access to Dewars Farm Quarry.

Constraints of the site will need further consideration including the potential impacts of further extraction on underlying water bodies, the nearby environmental designations, and on health and amenity, particularly given that the site lies in close proximity to a number of other existing minerals and waste operations, including the Ardley ERF. A sufficient stand-off distance from sensitive receptors is likely to be required which may reduce the workable area and impact the site’s viability.

Notwithstanding this, the site may have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

These nominations are for extensions to the existing Dewars Farm Quarry. This is an operational limestone quarry, originally permitted by an appeal decision dated 04/08/2004, with a quarrying end date of 2020. The currently active permission for Dewars Farm Quarry is:

MW.0102/18, permitted 29.04.2019: Section 73 application for the continuation of development permitted under 15/01660/CM (MW.0123/15) (for the winning and working of limestone and clay at Dewars Farm as an extension to Ardley Quarry) without complying with conditions 1 and 2, to allow the quarry to continue operating beyond 2020, to permit working until 2028 and restoration by 2029.

Conditions require: The development shall cease no later 31st December 2028; restoration shall be completed by 31st December 2029.

This application stated that 2.5 million tonnes of permitted reserve remained to be worked at the end of 2017; that the current rate of production is approximately 250,000tpa; and that it will take approximately 10 years to work the remaining reserve.

Part of the Dewars Farm Quarry has temporary permission for storage and distribution of incinerator bottom ash aggregate (IBAA) from the adjacent Ardley ERF plant: MW.0074/14, permitted 10.10.2004.

The storage of IBAA is required to cease by 31.12.2020 and the hardstanding to be removed and the site restored by 31.12.2021.

Dewars Farm Quarry and site nomination CR-13 adjoin the Ardley waste management site (see waste site nomination 287) but that is a separate site, with separate access, and the planning history of that site does not directly relate to these site nominations for mineral working.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole samples taken from the banks of the M40 running north and south of the eastern boundary show evidence of limestone deposits, albeit with some clay content. Other samples show cleaner oolitic limestone and forest marble at shallow depths. Fair – Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats identified within or adjacent to the site. However, notable habitats include the adjacent woodland, waterbodies and brook.

European protected species within and adjacent to the site include Great Crested Newt and several different bat species. Other protected and notable species include several mammals, birds, amphibians, plants and invertebrates.

Local designations include the Trow Pools and Ardley Fields Pond East. Local Wildlife Sites (LWS). Numerous other LWS have been identified within 1km of the site. The site is within Ardley and Upper Heyford Conservation Target Area (CTA).

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors.

Compliance with Policy C8: Landscape - Landscape Officer Assessment Site is not within a designated landscape or its setting. It comprises intensive agricultural fields on gently undulating ground bounded by Gaggle Brook and woodland belt (west & south), M40 (east) and railway line (north). The western boundary of the site and Trow Pool woodland at south eastern end are important landscape features.

Site comprises characteristic use and boundaries but landscape context of Ardley incinerator and M40 reduce landscape sensitivity.

PRoW runs along western boundary (Gaggle Brook) with views into the site. Occasional view from M40 possible but site will be viewed in context of incinerator and other activities.

Mitigation in the form of native planting and bunding is likely to assist in mitigating visual impacts.

Impacts on historic landscape character are not expected.

Due to the landscape context of incinerator, landfill, quarry and M40 the impact of the development on landscape character and views is considered to be slight. Extraction work should ensure the retention of existing mature vegetation along the western boundary (Gaggle Brook) and Trow Pool. Restoration has the potential to deliver landscape enhancements in the long term.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site would rely on the existing access to B430 (Freight Priority Network - Tertiary). However, the B430 is getting busier with Heyford Park development. HGVs would have to pass through Ardley to the north or Middleton Stoney to the south, both which have existing problems with the volume of traffic and congestion as the B430 used as a rat-run to avoid M40 junction 9. There is a potential for air quality issues to arise at Middleton Stoney.

© Adams Hendry Consulting Ltd. 356 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 The existing access has good visibility, and gates are set well back. The is a right turn filter lane to the site from the B430.

Conclusion

The site is nominated as a proposed extension to Dewars Farm Quarry and lies within the Mineral Strategic Resource Area (North West Bicester). It has potential to access directly onto the Oxfordshire Lorry Route Network (B430) via the existing access to Dewars Farm Quarry. Any increase in HGV trips have the potential to effect nearby villages. Whilst not in an AQMA, nitrogen dioxide levels in Middleton Stoney are quite high and are being monitored by Cherwell District Council and the County Council with a view to exploring various transport measures to stop levels increasing. It is likely that a routing agreement to divert traffic away from Middleton Stoney would be required if the site was allocated.

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors. Due to the landscape context of incinerator, landfill, quarry and M40 the impact of the development on landscape character and views is considered to be slight.

Site CR-15: Land off the B4100, Baynards Green

Site Information (as nominated in 2008) Site Location Land off the B4100, Baynards Green

Grid Reference SP539294

Administrative Area Cherwell

Parish Ardley

Site Nominee(s) David Einig Contracting

Proposed Development Crushed rock extraction. Potential new quarry. Site Area 15 ha Estimated annual 150,000 tpa output Estimated Reserves Estimated total yield of 4.5 mts. (including depth/ Estimated working depth of 15m Estimated overburden of 2.5m overburden) Proposed Restoration Progressive restoration to agriculture.

Access Existing access onto B4100 straight onto Junction 10 of the M40. Estimated 25 loads per day Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies in Mineral Strategic Resource Area (North West Bicester). Strategy – Strategic Resource • Site lies within the northern part of the County (Cherwell). Areas (Policy M3) • Site is proposed as a potential new quarry. • Estimated site yield is 4.5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • The site does not lie within 3km of an AONB. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a Principal aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • The site lies within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • There are no heritage assets within 500m of the site. • There are currently no known archaeological constraints to this allocation. • No impact on historic character expected. Transport and Access (Policy • The site access would be onto the B4100, a local access route on the Oxfordshire Lorry Route. C10) • Site lies 850m from the A43 which links to Junction 10 of the M40. • Site lies within close proximity to areas known for AM and PM traffic congestion (local roads around Baynards Green). • The site does not lie within an area with history of RTIs. Public Rights of Way (Policy C11) • A public right of way crosses the north west corner of the site. A further public footpath runs adjacent to the eastern boundary of the site. Health and Amenity (Policy C5) • Site lies approximately 115m from commercial units to the west and 150m of a residential property located to the north east of the site. Green Belt (Policy C12) • The site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 1 existing waste site: Ardley Landfill, ERF and HWRC. (minerals and waste sites) • No existing minerals sites lie within 3km of the site. • Site lies within 3km of 2 nominated waste sites: 278 Land off the B4100 Bayards Green and 287 Ardley Fields. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site was nominated in 2008 as a potential new quarry within the Mineral Strategic Resource Area (North West Bicester). The site has potential to access directly onto the Oxfordshire Lorry route Network (B4100).

Due to the time elapsed since the site’s nomination there is uncertainty regarding its current availability.

There appears to be no significant constraint to mineral development at the site and therefore it is considered to have potential for mineral development and will subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

BGS borehole records along the northern boundary indicate a shallow overburden overlying broken yellow limestone mottled with clay. Records along the southern boundary show shallow weak to moderately strong limestone cobbles with gravel and high silt and sand content.

Poor.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

No irreplaceable or notable habitats have been identified neither within or adjacent to the site. However, the presence pf European protected species of bat have been recorded within 2km, and other protected and notable species including several birds and mammals have been recorded.

The closest Local Wildlife Site is Stoke Woods, approximately 1.5km to the south-east of the site.

Overall ecological impacts are likely to be low, however will need to be informed by survey. No likely impacts on statutory or non-statutory sites of nature conservation interest are expected.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. It is proposed as a new stand-alone quarry which will result in the loss of one intensively farmed arable field. Allocation of this site would introduce quarrying on the eastern side of the M40 into an area where it currently does not exist.

No context of other quarries on this Eastern side of the M40 but Ardley quarry / Dewars Farm quarry a short distance on the other side of the M40.

The landscape sensitivity is reduced by detracting influences such as the proximity of the motorway junction and the proximity of the M40 and the B4100, which border the field on western and eastern side respectively.

© Adams Hendry Consulting Ltd. 362 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Site is also nominated as a permanent recycling site which, if successful, will result in no landscape restoration in the long term. Despite the low landscape sensitivity the impact is considered to be moderate due to the isolated and likely permanent nature of the impact.

The open plateau landscape with low hedges would allow long views in many places. There would be occasional views from the B4100 and M40.

The overall landscape and visual impact of the proposal is considered moderate due to this being a new site, its unconnected nature in the landscape, the impact on public views and the likelihood that there will be no restoration in the long term if permanently used for waste management uses.

Compliance with Policy C10: Transport - Highways Officer Assessment Site would use existing access to B4100 (Freight Priority Network - Tertiary) which would require improvement through the addition of a right turn filter lane. The B4100 is often congested at Baynards Green roundabout, but no towns or villages would be directly affected.

The site is approximately 850m from the A43 and 2km from the M40.

Conclusion

Whilst the site does lie within the Mineral Strategic Resource Area (North West Bicester), it is nominated as a new site on the eastern side of the M40. Policy M3 of the Core Strategy makes it clear that the priority is for the extension of existing sites before working new sites.

The site has good access to the Oxfordshire lorry route network; however mitigation may be required at Baynards Green roundabout.

The overall landscape and visual impact of the proposal is considered moderate as a new site, unconnected nature in the landscape, the impact on public views and the likelihood that there will be no restoration in the long term. Overall ecological impacts are likely to be low.

Site CR-19: Dewars Farm Quarry South Extension

Site Information (as nominated in 2018) Site Location Dewars Farm Quarry South Extension Grid Reference SP538243 Administrative Area Cherwell Parish Middleton Stoney Site Nominee(s) Smith and Sons (Bletchington) Ltd

Proposed Development Crushed rock extraction. Potential extension to Dewars Farm Quarry. Site Area 31 ha

Estimated annual 250,000 tpa output Estimated Reserves Estimated total yield is 2.2 mts (including depth/ Estimated working depth at 5-10m Estimated Overburden of 1.5m overburden) Proposed Restoration Low level agricultural use with biodiversity enhancements including open water ponds on the low ground adjacent to the Gagle Brook with marginal habitats managed for wildlife. Access Existing purpose built Dewars Farm Quarry access on to the B430. Estimated c. 95 lorry movements (in and out) per Traffic day. Movements Year of Development would have to start Commencement around 2025 before the exhaustion of existing consented reserves in 2027. Lifetime of 9-10 years. End date for extraction Operation 2027 (latest).

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Area (North West Bicester). Strategy – Strategic Resource • The site lies within the northern part of the County (Cherwell). Areas (Policy M3) • Site is proposed as a potential extension to Dewars Farm Quarry. • Estimated site yield is 2.2 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies adjacent to the Ardley Trackways SSSI. (Policy C7) • Site lies within 1km of the Ardley Cutting and Quarry SSSI • Site lies within 300m of the Ardley Fields Quarry Local Geological Site. • Site lies within 1km of a proposed Local Wildlife Site (Ardley Fields Quarry). • Site lies within 1km of Ancient Woodland. • Site lies within 3km of a Local Nature Reserve. • Site lies in excess of 5km from International/European designated sites. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • The site is largely within flood zone 1. The north east corner of the site lies within flood zones 2 (Policy C3 and Policy C4) and 3. • Site not within a source protection zone. • Site overlies a principal aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 3 agricultural land. • Restoration proposed. Historic Environment (Policy C9) • Site lies within 300m of Grade II listed buildings (Lodge Farmhouse and Trow Pool Water Tower). • Grade II listed Park and Garden (Middleton Park) within 2km to the south. • Site does not lie in close proximity to a conservation area. • Site lies within 900m of a Scheduled Monument (Middleton Stoney Castle). • The site is located in an area of considerable archaeological interest. Archaeological investigations for the current extraction area at Dewars Farm have revealed extensive evidence of later prehistoric activity including a settlement area and a pit alignment along with an Anglo-Saxon cemetery. • There are currently no known historic landscape constraints. Transport and Access (Policy • The site lies adjacent to the Oxfordshire Lorry Route Network (B430), a local access road. C10) • The M40 is with 3km of the site and adjoins its eastern boundary • Access would be via the existing access at Dewars Farm Quarry.

© Adams Hendry Consulting Ltd. 366 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • AM peak or PM peak traffic congestion areas identified within proximity to site. Public Rights of Way (Policy C11) • One public footpath crosses the site south west to north east. A further footpath is adjacent to the eastern boundary • Restoration proposed. Health and Amenity (Policy C5) • There are residential properties which lie within 50m south of the site (Dewars Farm). • An allotment is with 300m of the site to the south west, north of Middleton Stony • Residential properties in Middleton Stony are approximately 500m south west of the site. Green Belt (Policy C12) • Site is not located within the Green Belt. Aerodrome Safeguarding (Policy • Site located within the London Oxford Airport aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Ashgrove Farm and Ardley Landfill. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Dewars Farm Quarry. • Site lies within 3km of 2 nominated waste sites: 226 Dewars Farm Quarry and 287 Ardley Fields. • Site lies within 3km of 1 nominated minerals site: CR-13.

Conclusion

The site is nominated as a proposed extension to Dewars Farm Quarry and lies within the Mineral Strategic Resource Area (North West Bicester). The site has potential to access to the Oxfordshire Lorry Route Network (B430) via the existing access to Dewars Farm Quarry.

Notwithstanding this, the site may have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Part of the Dewars Farm Quarry has temporary permission for storage and distribution of incinerator bottom ash aggregate (IBAA) from the adjacent Ardley ERF plant: MW.0074/14, permitted 10.10.2004. The storage of IBAA is required to cease by 31.12.2020 and the hardstanding to be removed and the site restored by 31.12.2021.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Very limited information available to assess quality. However, the adjacent mineral working demonstrates a potentially viable resource. A borehole log 500m to the north east of the site indicates the presence of shallow sand deposits. Fair

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Irreplaceable habitats adjacent to the site include the Ancient Woodland, located 180m to the south. Additionally, notable habitats include the adjacent woodland, waterbodies and brook to the site.

There are a number of bat species recorded in the local area and records of Great Crested Newts that are both protected by European legislation. Other notable and protected species in the local area include mammals, birds, amphibians, plants and invertebrates.

The site lies adjacent to the Trow Pools Local Wildlife Site (LWS). There are numerous other LWSs within 1km of the site. The site is within Ardley and Upper Heyford Conservation Target Area (CTA).

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors. There is potential for useful biodiversity gains and improvements for the surface water quality.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting.

Extension to existing quarry comprising several medium-sized intensively farmed fields. Low hedgerow boundaries within site, mature hedgerows and trees along B430. Gaggle Brook with associated mature vegetation forms the eastern boundary and is important feature in this otherwise open landscape.

Existing quarry/landfill/ incinerator north of the site together with HGV movements, pylons and M40 are existing detractors in the landscape that influence perception and reduce landscape sensitivity.

Site comes close to Middleton Stoney (approximately 250m).

Occasional or glimpsed views from B430, Middleton Road and Middleton Stoney are likely but site will mostly be viewed in context of other existing industrial uses such es existing quarrying, incinerator. Mitigation in the form of native planting and bunding will assist in mitigating visual impacts from road but is unlikely to be fully successful in mitigating impact on all views. Existing mature vegetation along the eastern boundary (Gaggle Brook) should be retained along with other characteristic boundary vegetation.

Overall the landscape and visual impact of the development is considered to be limited due to the strong influence of detractors in the landscape context of the site (e.g. existing quarry, waste processing, HGV movements, pylons, M40 etc).

Compliance with Policy C10: Transport - Highways Officer Assessment

The site would rely on the existing access to B430 (Freight Priority Network - Tertiary). However, the B430 is getting busier with Heyford Park development. HGVs would have to pass through Ardley to the north or Middleton Stoney to the south, both which have existing problems with the volume of traffic and congestion as the B430 used as a rat-run to avoid M40 junction 9. There are already high volumes of traffic through Ardley and Middleton Stoney and potential for air quality issues to arise at Middleton Stoney.

The existing access has good visibility, and gates are set well back. The is a right turn filter lane to the site from the B430.

Conclusion

Site SG-08 – Lower Road, Church Hanborough

Site Information (as nominated in 2018) Site Location Lower Road, Church Hanborough Grid Reference SP433121 Administrative Area West Oxfordshire Parish Hanborough and Eynsham Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 210 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield of up to 2.5 mts (including depth/ Estimated overburden of 1.2m Estimated working depth of 2.4m overburden) Proposed Restoration Possible to restore to agriculture at low level &/or to realise a mosaic of wetland habitats with nature conservation interests using progressive restoration techniques. Access Access off road leading North from Eynsham roundabout, linking A40 & A4095. Vehicular access possible and can be linked with overall Garden village development. Estimated Unknown Traffic Movements Year of Anytime in plan period from 2022 Commencement onward – flexible to suit conditions. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy (Policy M3) Valleys) in accordance with Policy M3. • Site is located in the northern part of the county (West Oxfordshire). • The site is not an extension to an existing quarry. • Estimated site yield is up to 2.5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan, however the southern boundary of the land parcel west of Lower Road and the western boundary of the southern land parcel east of Lower Road are located adjacent to the Cotswold Garden Village allocation, west of Lower Road. • West Oxfordshire DC have raised concerns regarding the relationship of these two sites, with particular emphasis on the potential impact on amenity. Biodiversity and Geodiversity • The Oxford Meadows SAC lies approximately 2.2km to the south-east of the site. (Policy C7) • Site located in excess of 1km from NNR. • Site located in excess of 500m from a SINC or LNR. • Ancient Woodland (Burleigh Wood) lies 90m to the northeast of the site and Bladon Heath lies within 750m to the northeast of the site. • A further Ancient Woodland (Pinsley Wood) lies 200m to the northwest of the site. • Blenheim Park SSSI and Proposed Local Wildlife Site lies 750m north of the site and Long Hanborough Gravel Pit SSSI lies 1km northwest of the site. • A Priority Habitat Creation and Restoration point lies 2km northwest of the site. • Site located in excess of 5km from a SAC or Ramsar Site. • The Berks, Bucks & Oxon Wildlife Trust advise that the site is immediately adjacent to City Farm LWS, a short distance from South Freeland Meadows LWS and in close proximity to a number of Ancient Woodlands (Pinsley Wood and Burleigh Wood), which are also designated as LWS. The nomination raises concerns with regard to indirect effects on these designated sites such as changes in hydrology, noise or atmospheric pollution. Landscape / Visual (Policy C8) • The Cotswolds AONB is located approximately 650m to the northwest of the site. Water Environment and Flooding • A large section of the site is within Flood Zone 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a principal and secondary aquifer. Air Quality (Policy C5) • Site lies over 4.5km from the nearest AQMA (Oxford). Soil Resources (Policy C6) • A central band of Grade 4 agricultural land runs north to south with pockets of Grade 3 agricultural land to the east and west. Historic Environment (Policy C9) • The Grade 2 Eynsham Mill is approximately 60m east of the site and there is a listed bridge adjacent to the site and another approximately 70m east of the site.

© Adams Hendry Consulting Ltd. 373 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • The Grade 2 listed Burleigh Farmhouse lies approximately 450m from the site. • Listed buildings at Church Hanborough lie approximately 200m west of the site and dwellings at City Farm lie approximately 300m south west of the site. • The Grade 2 listed Mill Farmhouse and attached mill building lie within the site near the northern boundary. • Two listed bridges lie approximately 500m north of the site. • Bladon Camp Scheduled Monument lies 1.4km north east of the site and Eynsham Abbey Scheduled Monument lies 1.2km south of the site. • Blenheim Palace (Grade I listed Park and Garden and World Heritage Site) lies approximately 750m north of the site. • Historic England have advised that the potential impact on the setting of the Conservation Area also needs to be considered in determining what area, if any, of the site is suitable for mineral extraction and that listed buildings should be excluded from the allocated area, with consideration also towards their setting. • No significant known constraints but the site is within an area of considerable archaeological potential. In the southern area of the site, a series of cropmarks have been identified These include a series of circular enclosures that are either small barrows or hut circles, pits and linear features. There is a further barrow on the west side of the allocation. There are further cropmarks of circular enclosures and linear features recorded to the north of the allocation. • Approximately 11.7 ha of the site lies within the Church Hanborough Conservation Area.

Transport and Access (Policy • Site is located within 500m of access onto the A40, via Lower road and the Eynsham C10) roundabout. • Lower Road is a single carriageway subject to a national speed limit restriction. • Site traffic is likely to impact on AM and PM congestion along the A40. • The site lies in close proximity to an area with a history of RTI’s. Public Rights of Way (Policy C11) • There is a footpath which enters to the north of the site and ends at the River Evenlode. • Restoration proposed which could contribute to green infrastructure network around new garden village. Health and Amenity (Policy C5) • Properties at Mill Farm appear to be included in the northernmost part of the site boundary. • There are also a number of residential properties in very close proximity and adjacent to the site including; Eynsham Mill and properties at New Wintles Farm which adjoin the south eastern boundary of the site; properties at the Church Road/Lower Road junction; properties on Lower Road between the three areas of the site and Goose Eye Farm which adjoins the eastern boundary. • Properties at Church Hanborough are 100m west of the site. Green Belt (Policy C12) • The majority of the site overlies Greenbelt land. The west area of the site is the only part outside of the Greenbelt. • Restoration proposed to restore to agriculture at low level and/or to realise a mosaic of wetland habitats with nature conservation interests.

© Adams Hendry Consulting Ltd. 374 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Aerodrome Safeguarding (Policy • Site falls within the London Oxford Airport aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of two existing waste sites: Worton Farm, and New Wintles Farm. (minerals and waste sites) • Site lies within 3km of one existing minerals site: Cassington Quarry. • Site lies within 3km of two nominated waste sites: 008 New Wintles Farm and 009 Worton Farm (Areas C & D). • Site lies within 3km of four nominated minerals sites: SG-20, SG-20a and SG-20b Land between Eynsham & Cassington, and SG-29 Sutton Farm. • The nearest M&W site is New Wintles Farm, within 400m to the west of the site. • The southern boundary of the land parcel west of Lower Road and the western boundary of the southern land parcel east of Lower Road lie adjacent to the Cotswold Garden Village allocation, west of Lower Road. • West Oxfordshire DC have raised concerns regarding the relationship of these two sites, with particular emphasis on the potential impact on amenity.

Conclusion

The site a potential new quarry and is located in the Green Belt. Given the scale of the site there may be the potential for the area of works to avoid, or reduce the impact on sensitive receptors identified above, particularly environmental designations, heritage assets and residential amenity.

The access to the site is proposed to be from via Lower Road. This route connects to the Oxfordshire Lorry route Network, the A4095 to the north and the A40 to the south.

The site may therefore have some potential for mineral extraction and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

No site planning history.

There are two former/existing mineral extraction and waste management sites to the south/west of this nomination • City Farm • New Wintles Farm and a former mineral extraction site to the east, at Purwell Farm.

City Farm Reserves at City Farm (to South West of the site) were worked out several years ago and the site is now in aftercare (MW.0095/17, permitted 30.01.2018) and currently in agricultural use.

New Wintles Farm This site is further south, beyond City Farm, and is an area of former gravel extraction and landfilling which has an active planning permission for a permanent waste (aggregate) recycling facility: MW.0002/17, permitted 08.03.2017.

Purwell Farm This site was worked out many years ago and no longer has any significance for this nomination.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Existing Borehole records show potentially viable sand and gravel resources in the northern section of the site and southern area of the southern section of the site. Limited records available in the western section, those which were recorded close to it show high clay content. Fair – good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Records of Notable Habitats within and adjacent to the site include adjacent woodland and the River Evenlode along part of eastern site boundary. Records of European protected species include Great Crested Newt and bats. Other Protected/Notable species include numerous records of mammal, bird, amphibian, plant and invertebrate.

© Adams Hendry Consulting Ltd. 376 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 There is significant potential to realise conservation and community accessible green space improvements, noting the proximity of the site to the proposed Cotswolds Garden Village to south and west. There is further potential to bridge the Pinsley and Burleigh ancient woodlands.

Overall the potential ecological impacts of the proposals are likely to be high. The site is large and in close proximity to several known sensitive ecological receptors, including ancient woodland, Local Wildlife Sites and the River Evenlode. Other ecological sensitivities will need to be assessed. The sites proximity to the SAC will require further detailed assessment. Overall, without evidence to the contrary, informed by thorough assessment, impacts on biodiversity are considered high and the proposals are considered unacceptable.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site boundary is approximately 800m from Cotswolds AONB however the site is separated from it by a railway line and other uses. No adverse impact on AONB is expected on a condition that HGV movement would not be routed that way.

This is a very large new site that comprises a number of large fields on either side of Lower Road. The site reflects the local landscape character of low- lying farmland with large open fields and strong structure of hedgerows, trees or tree belts. Internal hedgerow boundaries are low giving a sense of openness. Large open fields with low hedgerows enable extensive views from Lower End Road.

The Western part of the site extends into Church Hanborough conservation area.

The large size of the site and associated HGV movements has potential to cause substantial and sustained impact despite likely phasing.

Considering the size of the site there are only few footpaths in the area that are likely to offer views into the site: • A PRoW runs along, or in short distance from, the western part of the western site; • A PRoW from Cassington meets the eastern boundary. Coming from higher ground, good views into the site are expected; and • A PRoW crosses the eastern site at its southern end.

Views from more distant PRoWs might also exist.

Traces of earlier landscapes are likely to have been removed across most of the site. However, the area of unenclosed rough ground in the north eastern corner is of historic importance and considered highly sensitive to development. Any archaeological features should be well preserved in this location. However this area of the site has been divorced from its previous surviving landscape which will have reduced its significance.

The overall landscape and visual impacts are considered to be potentially substantial due to the large size of the site, it being a new site (not an extension), the introduction of intrusive development into what’s currently tranquil countryside, its impact on Church Hanborough conservation area, the expected long duration of workings as well as indirect effects caused by the increase in HGV movements on nearby roads.

Visual effects are likely to be moderate but in the context of the anticipated landscape impacts may potentially be substantial.

There are also several other mineral sites proposed in the area.

Compliance with Policy C10: Transport - Highways Officer Assessment The three parcels of land comprising the site nomination are 2km or less to A40 (Freight Priority Network - Primary). There is potential to widen/improve Lower Road. The route to the A40 does not pass through any villages.

New or improved access will be required for each of the three parcels. There may not be sufficient space to incorporate right-turn filter lanes on Lower Road.

There are slight issues with access to the Oxfordshire Lorry Route network that are capable of resolution and may require some mitigation.

However, the Hanborough Station infrastructure study (the Hanborough Hub study) is a piece of work commissioned by West Oxfordshire District Council with OCC involvement and will identify opportunities to improve access to the station by all modes and will also inform planning guidance that will shape development of the station into a transport and mobility hub, in line with Policy EW10 and paragraph 9.5.110 of the Local Plan.

This is a key priority for both councils as it supports development of the Cotswolds Garden Village. It also complements the work being done by the North Cotswold Line Taskforce on the wider strategic importance of the railway and the business case for investing in a more frequent train service and expanded station facilities for Hanborough.

The area of Site SG-08 that lies west of Lower Road will significant hinder the ability to provide any kind of direct route for buses, cyclists, pedestrians or Connected Autonomous Vehicles (CAV) between Cotswold Garden Village and Hanborough station.

Conclusion

This is very large, new site within the Green Belt and in close proximity to the AONB comprising of three parcels of land. As the allocation of the western parcel of land may hinder the public transport corridor proposals between Hanborough Station and the Cotswold Garden Village in line with Policy EW10 and paragraph 9.5.110 of West Oxfordshire Local Plan, it is considered that this part of the site is not suitable for allocation.

Having regard to the detailed appraisal of the landscape and ecology specialists, it is evident that mineral working on the eastern and southern parcels may have potential to have a significant impact on biodiversity and landscape without mitigation.

Whilst the close proximity of the site to the proposed Cotswold Garden Village, may offer a potential local market for mineral supply and beneficial opportunities if the site were to be worked (subject to careful phasing to avoid any adverse impacts on local amenity) and potential opportunities to secure biodiversity gain and improved countryside access, the allocation of the site may give rise to cumulative environmental effects both individually and in combination with other existing mineral and waste sites as well as the proposed Cotswold Garden Village. There are also a number of nominated sites in the vicinity.

The Core Strategy acknowledges that the rate and intensity of mineral working and the consequential cumulative impacts on local communities, including

© Adams Hendry Consulting Ltd. 378 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 the generation of traffic, particularly on the A40, and impacts on local rivers and ground flows are of concern in Western Oxfordshire.

As the site is a nomination for a new site in the Green Belt and not a proposed extension to an existing site and is located in the northern part of the County where the requirement for additional sand and gravel provision for the plan period is relatively small, there may be other potential options to meet sharp sand and gravel requirements within the Thames, Lower Windrush and Lower Evenlode Valleys area that may offer a more sustainable location for mineral working in accordance with Policy M4 of the Core Strategy.

© Adams Hendry Consulting Ltd. 379 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Final Site SG-09 & SG-59 – Land north of Drayton St Leonard and Berinsfield and land at Stadhampton

Site SG-09 & SG-59: Land north of Drayton St Leonard and Berinsfield and land at Stadhampton

Site Information (as nominated in 2018) Site Location Land north of Drayton St Leonard and Berinsfield and land at Stadhampton Grid Reference SU 597981 Administrative Area South Oxfordshire Parish Stadhampton and Drayton St. Leonard Site Nominee(s) D.K. Symes Associates (agent) Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 225 ha Estimated annual 175,000 – 200,000 tpa output Estimated Reserves Estimated total yield of 6.0 mts (including depth/ Estimated working depth of up to 6.0m overburden) Estimated overburden of 1.0m

Proposed Restoration Progressive restoration will be carried out to a mix of farmland, wet and dry woodland and wetland habitat. Access An upgraded access onto the A4074 is proposed. Estimated 120 daily (60 in, 60 out) Traffic Max daily movements 160 (80 in, 80 out) Movements Year of Upon grant of Planning Commencement Permission. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Both sites are located within the Mineral Strategic Resource Area (Thames, Lower Thame Strategy – Strategic Resource Valley – Oxford to Cholsey) in the southern part of the County (South Oxfordshire). Areas (Policy M3) • Site is a potential new quarry. • Estimated total yield of 6.0 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • South Oxfordshire District Council’s submission Local Plan also includes a housing allocation of 1,700 homes to the east of Berinsfield. Biodiversity and Geodiversity • Ancient Woodland 180m to the east of the site. (Policy C7) • Site SG-09 lies 3.9km to the north of Little Wittenham SAC, site SG-59 lies approximately 4.8km to the north of Little Wittenham SAC. • Site located in excess of 1km from SSSI, NNR and protected species. • Site located in excess of 500m from a SINC, LNR, Local Wildlife Site or Local Geological Site. • Priority Habitat Creation and Restoration Point 3.5km south of SG-09. • The Berks, Bucks and Oxon Wildlife Trust have advised that the nominated site lies adjacent to the River Thame raising concerns about impact on hydrological flows that might potentially affect habitats and species downstream. This nomination might also adversely impact on the work being done along the River Thame and consultation with the River Thame Conservation Trust is recommended. Landscape / Visual (Policy C8) • Site lies within 3km of the North Wessex Downs AONB. Water Environment and Flooding • Approximately half the site lies within Flood Zones 2 and 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. • Site lies adjacent to the banks of the River Thame and Baldon Brook • Potential flood storage as part of afteruse / restoration. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of primarily Grade 2 and 3 agricultural land with small pockets of Grade 4 agricultural land. Historic Environment (Policy C9) • Grade II listed properties in Brookhampton lie within 15m to the north of the site. • Grade II listed buildings in Chiselhampton lie within 25m north of the site (on the opposite side of the river). • Grade II listed properties in Stadhampton lie within 200m north of the site. • Grade II listed Church of St Leonard lies 100m south of the site in Drayton St Leonard. • Ascott Park (Grade II listed Park and Garden) lies 600m east of the site.

© Adams Hendry Consulting Ltd. 382 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Nuneham Courtenay (Grade I listed Park and Garden) lies 2.9km west of the site. • Scheduled Monuments lie 1.9m south of site (Church Piece Cemetery Site), 2.4km south of the site (Rungs, ditches) and 2.4km west of the site (site of Roman Kilns). • Battlefield 4km east of the site. • Historic England advise that the site – SG-09 – contains a monument equivalent to a Scheduled Monument, which is afforded the same protection by the National Planning Policy Framework. • Historic England also advise that SG-59 may be within the setting of the Grade II* listed Camoys Court and/or the Grade II listed and scheduled Chiselhampton Bridge, the potential impact on the significance of which should be taken into account in deciding whether or not this site, or part of it, is suitable for mineral extraction. • Site does not lie within or in close proximity to a conservation area. • The site is within an area of considerable archaeological potential and includes evidence of a well-preserved historic landscape dating to the prehistoric period. Evidence exists of a Neolithic cursus, other funerary monuments and barrows, A Roman Road and a probable Roman settlement site. • Elements of the historic landscape appear to be demonstrably of equivalent significance to scheduled monuments and would need to be physically preserved. Transport and Access (Policy • Site lies approximately 2.3km to the east of the Oxfordshire Lorry route Network (A4074). C10) • An upgraded access onto the A4074 is proposed. Public Rights of Way (Policy C11) • Two public footpaths enter the site and one public bridleway. • Restoration of original lines proposed where possible. Health and Amenity (Policy C5) • A pair of semi-detached dwellings on Newington Road appear to be within the site boundary in the north eastern corner of the site. • Dwellings on Stadhampton Road lie adjacent to the southern site boundary. • Residential dwellings at Brookhampton lie approximately 10-15m east of the site (on the other side of Newington Road) • Dwellings at Drayton St Leonard lie within 15m south of the site and dwellings at Chiselhampton lie within 25m north of the site (on the opposite side of the river). Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the Dalton Barracks buffer of airport safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Berinsfield Car Breakers and The Metal Yard Nuneham Courtenay. waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of one nominated waste site: 286 Wally Corner. • Site lies within 3km of one nominated minerals site: SG-13 Land at Shillingford.

Conclusion

The key constraints affecting the nominated sites are proximity to residential receptors in Berinsfield, Brookhampton, Stadhampton and Chiselhampton. The site also lies adjacent to a number of water bodies including the River Thame and Baldon Brook. However, due to the scale of the site there is potential to provide adequate stand-off and protection buffers from these receptors.

The monument should be excluded from any potential area for mineral extraction and, although the monument occurs in the western area of the site and covers only a small area, consideration should also be given to the setting of the monument in determining what area of the site, if any, may be suitable for mineral extraction.

Access to the Oxfordshire Lorry Route Network can potentially be provided through a new access stemming from the western boundary, heading west to the A4074.

Due to the scale of the site and the potential to provide appropriate mitigation, and the sites location within the Mineral Strategic Resource Area (Thames, Lower Thame Valley – Oxford to Cholsey), the site is considered to have potential for mineral development and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource Existing borehole layers over the site demonstrate a relatively high level of overburden. Borehole records taken from the upper western section of SG-09 indicate a high clay content, records taken form the south of this section show greater sand and gravel quality. Borehole samples within the eastern section of SG-09 demonstrate good quality. Borehole record taken from the northern end of SG-59 demonstrate good quality. Fair – Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no know irreplaceable habitats within or adjacent to the site. Notable habitats include adjacent woodland and watercourse (Thames)

Records exist for European protected species including Great Crested Newt and several bat species in local area.

Records exist for other protected/notable species including several protected and notable mammal, bird, amphibian, plant and invertebrate species.

Closest Local Wildlife Site is Dorchester Gravel Pits located approximately 2.5km (SG09) and 1.8km (SG59) to the south-west. Thames Clifton to Shillingford Conservation Target Area is approximately 1.7km (SG09) and 2.5km (SG59) to the south-west.

Potential improvements to surface water quality and habitats. Wider potential for improving accessible green space given proximity to Berinsfield development area and adjacent communities

Overall the ecological impacts of the proposals are likely to be low. No significant impacts on any statutory or non-statutory site of nature conservation interest are anticipated. Biodiversity net gain to be achieved on site or adjacent.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting.

Site is a new allocation in a currently low lying tranquil agricultural area of medium-sized fields with low/gappy hedgerows and some scattered ash and willow trees. River Thame and Baldon Brook and associated vegetation are important features in the landscape and subject to a conservation project (River Thame Conservation Trust).

Site extends to the edge of the settlements of Brookhampton and Drayton St Leonard affecting their setting.

A PRoW runs along the southwestern boundary of SG-09 before crossing it. It continues a short distance west of SG-59 with views into the site. SG-09 is crossed by further footpath at its southern and western end.

A network of PRoWs exist around Brookhampton, Chiselhampton, Newington, Drayton St Leonard and Berinsfield with likely views into the site.

There would be views across the site from Stadhampton Rd, a rural lane between Brookhampton and Drayton St Leonard and from other roads in the surrounding area. There would also be views of the site from residential properties in nearby settlements..

Overall the landscape and visual impact of this site allocation is considered to be substantial due to it being a new site, its large size, the absence of industrial uses in the area, the introduction of intrusive uses into an area that is currently rural and tranquil, the impact on users of local footpaths and local roads, and the proximity and resulting impact on local the local settlements of Chiselhampton, Brookhampton and Drayton St Leonard.

Compliance with Policy C10: Transport - Highways Officer Assessment

Highway network known to have capacity issues in the peak times

Conclusion

The site lies within Southern Oxfordshire and within the strategic resource area and therefore allocation would accord with the principles set out in Core Strategy Policy M3. However, the site is a significant site within the Green Belt where mineral extraction is only considered appropriate development if it preserves the openness of the Green Belt and does not conflict with the purposes of including land within it. Given the size of the nominated site, the landscape and visual impact is considered to be substantial and there is a risk that it would erode the gap between Drayton St Leonard, Newington and Stadhampton.

The site is in an area of high archaeological potential and therefore further assessment would need to be undertaken to determine whether any mineral extraction would be possible without having a significant adverse impact on the historic environment.

There are capacity issues on the highway network at peak times which would need to be mitigated should this site be allocated.

© Adams Hendry Consulting Ltd. 386 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Final Site SG-11 & SG-65 – Land situated Northeast of Sonning Eye (Caversham phases ‘D’ & ‘E’)

Site SG-11 & SG-65: Land situated Northeast of Sonning Eye (Caversham phases ‘D’ & ‘E’)

Site Information (as nominated in 2018) Site Location Land situated Northeast of Sonning Eye (Caversham phases ‘D’ & ‘E’) Grid Reference SU752764 Administrative Area South Oxfordshire Parish Eye and Dunsden and Shiplake Site Nominee(s) Tarmac Aggregates Limited Proposed Development Sharp sand and gravel extraction. Extension to Caversham Phase C scheme. Site Area SG-65 is 70 ha SG-11 is 16.5 ha Estimated annual The existing site has a maximum output capacity of 170,000 tonnes of aggregates processed and sold per annum, with a typical output at or around 130,000 tonnes per annum. Estimated Reserves Estimated total yield of 2 mts (including depth/ Estimated working depth of up to 10m overburden) Estimated overburden of 2m Proposed Restoration The site will be restored to a mixture of high-quality agricultural land with floodplain habitats. Wherever possible Grade 2 and 3a land will be restored to its original quality. Lower quality agricultural land will be used to establish alternative wetland habitats consistent with local and national BAP targets. Access The access onto the B478 (Playhatch Road) will be used to distribute the minerals to the market via the A4155. Access for imported materials, is likely to be off the A4155 to the

© Adams Hendry Consulting Ltd. 388 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 north via a new access that has been approved as part of the Phase C scheme. Estimated Typically 40 loads or 80 movements Traffic per day. Based on maximum activity the scheme would generate 55 Movements loads or 110 movements per day. These would be a combination of ready mixed concrete trucks,18 tonne tipper units and 6 tonne LGVs, with tanker deliveries for the ready mixed concrete plant at the plant site that would be retained through the duration of any scheme. Year of 2029/2030 Commencement Lifetime of 12 years Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site located within Mineral Strategic Resource Area (Thames Valley – Caversham to Shiplake) Strategy – Strategic Resource in the southern part of the county (South Oxfordshire). Areas (Policy M3) • Site proposed as a potential extension to Caversham Quarry. • Estimated total yield of 2.0 mts District Local Plan Allocation • Site is not allocated in a District Local Plan. • The Central and Eastern Berkshire Authorities advise that the site is on the border between Oxfordshire and Central and Eastern Berkshire. Biodiversity and Geodiversity • Site located in excess of 5km from International / European designated sites. (Policy C7) • Site located in excess of 1km from SSSI, NNR and protected species. Nearest SSSI (Harpsden Wood) is 2.4km north of the site. • Site lies within 25m of ancient woodland (Spanhill Copse) to the west. 4 other areas of Ancient Woodland lie within 1km northwest of the site. • Proposed Local Wildlife Site (Span Hill Chalk Pit)/ Span Quarry Local Geological Site lies 400m west of the site. • Ali’s Pond LNR lies 1.3km south of the site and Clayfield Copse lies 2.4km west of the site. • Natural England advise that the site supports Priority Habitats (deciduous woodland and coastal floodplain grazing marsh). • Berkshire, Buckinghamshire and Oxfordshire Wildllife Trust advise that SG-65 directly affects Shiplake Marsh LWS (77T02/10), which comprises rare marshy grassland. It is also in close proximity to Warren Wood LWS (77T01), an ash woodland with rare wetland habitats at the base of the slope, and Spanhill Copse AW. In addition the nominated sites are partly located within the Loddon Valley Gravel Pits Biodiversity Opportunity Area and the Thames Valley Environmental Records Centre hold a number of protected and notable species records for the area. As such we consider this site sensitive in ecological terms. Landscape / Visual (Policy C8) • Site lies within 1.3km of the Chilterns AONB. Water Environment and Flooding • Site lies within Flood Zone 2 and 3. (Policy C3 and Policy C4)) • Approximately 50% of the site to the east lies within source protection zone 3. Air Quality (Policy C5) • Site lies 1.5km from AQMA. Soil Resources (Policy C6) • SG-11 primarily lies in an area of Grade 2 agricultural land. • SG-65 is primarily Grade 4 agricultural land with a small pocket of Grade 3. Historic Environment (Policy C9) • Historic England advise that Site SG-11 is likely to be within the setting of the Sonning Eye Conservation Area to the south of the site, the potential impact on which will need to be assessed.

© Adams Hendry Consulting Ltd. 390 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Grade II listed buildings lie within 165m south of the site in Sonning Eye. • Cropmark complexes lie within 1km southeast of the site (scheduled ancient monuments). • Caversham park (Grade II listed) lies 2km west of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • The site is within an area of archaeological potential. Archaeological deposits have been recorded within the current application site and the cropmark evidence suggests that further archaeological features are present within the site. • On the north west side is an area recorded as ancient (pre C18th) enclosure. It is however divorced from its previous surviving landscape which will have reduced its significance. As such there are currently no known historic landscape constraints.

Transport and Access (Policy • Site has access to the A4155, identified as local lorry route access. C10) • It is proposed that the minerals will be processed at the existing plant site at the Sonning works. Minerals will be transported from the extraction area to the works using a conveyor. • The A4155 goes past residential properties and a school in Shiplake to the north east and through Playhatch to the south west. • The B478 through Sonning Eye is subject to a weight restriction (7.5t) at a bridge crossing when the road width narrows to a single carriageway. • There is no history of any serious or fatal RTI’s within 3km of the site. • No AM peak or PM peak traffic congestion identified within proximity to site. • Wokingham Borough Council expresses concerns regarding HGV routing relating to this site. Further detailed assessment is required having regard to the weight restrictions that are in place on existing bridges between Reading and Henley. Public Rights of Way (Policy C11) • A section of the Thames Path is located within Site SG-65. • Promotor indicates potential for permissive Right of Way to be included as part of restoration. Health and Amenity (Policy C5) • Residential dwellings in Sonning Eye within 95m south of site off B478 and Spring Lane. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site does not lie within an aerodrome safeguarding area. M10)

Cumulative Impact (minerals and • Site lies within 3km of two existing waste sites: Caversham Quarry Extension and Playhatch Quarry. waste sites) • Site lies within 3km of one existing minerals site: Caversham Quarry. • Site lies within 3km of one nominated waste site: 005 Playhatch Quarry. • There are no nominated minerals sites within 3km of the site. • Potential cross boundary, cumulative impacts with Reading will need to be considered.

The nominated quarry site(s) lie adjacent to the north and southwest of Caversham Quarry and is within the MSRA. The existing access to Caversham Quarry is from the A4155. The A4155 is a local access road. The rate and intensity of mineral working in this area and the cumulative impact of further works on local communities (in particular Shiplake, Playhatch and Sonning Eye) including the generation of traffic, will need to be assessed in further detail.

Other constraints also have the potential to impact mineral development at this site including potential impacts on biodiversity, heritage and agricultural land. The Thames Path recreational route cuts across part of SG-65.

Given the site’s location within the MSRA, the site is considered to have potential for further mineral extraction and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is a long history of sand and gravel working at Caversham Quarry. The original quarry was to the south of the A4155 and B478, south west of the nominated site. That area has been worked out and restored, apart from the current processing plant site which is located on the north eastern part of that area.

More recently, the triangle of land between the A4155, B478 and Spring Lane, west of the nominated site, was worked for sand and gravel under permission MW.009/08 granted 18.03.2009. That area is now being restored.

The current operational mineral working area, known as Caversham Phase C, is immediately to the north and west of the nominated site. This area is permitted by application MW.0158/11, granted 20.08.2014, for extension to Caversham sand and gravel quarry with restoration to agriculture and flood plain habitats using suitable imported inert restoration material and construction of a new access off the A4155. Conditions require: • Extraction of minerals shall cease by 31.12.2027; • Deposit of waste shall cease by 31.12.2029; • Restoration shall be completed by 31.12.2029.

The total permitted reserve is 1.86 mt of sand and gravel. Mineral extraction from Phase C commenced in 2017 and most of the reserve has yet to be worked. Extracted mineral is transported by conveyor to the processing plant and site access to the east, on the south side of Playhatch Road (B478). The processing plant has a capacity of 170,000 tpa and average annual output is estimated as 130,000 tpa.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Limited borehole records available to assess quality. Records for the northern boundary of the site indicate limited sand and gravel content and high indication of chalk and clay. Records available within 250m of the site boundary show sand and gravel deposits, including one near to the banks of the R. Thames which demonstrates a significant sand and gravel deposit with limited fines. Poor - Fair

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Records of irreplaceable habitats include several areas of ancient woodland, the closest being adjacent to the northern boundary of SG65 and approximately 400m north of SG11.

Notable habitats within and adjacent to the site include records of several areas of woodland. The site in close proximity to waterbodies and the River Thames.

European protected species within or adjacent to the site include Great Crested Newt and several bat species

Ali's Pond Local Natural Reserve lies approximately 1km south-east. Several Local Wildlife Sites (LWS) and potential LWSs are within 2km. SG11 is within the Shiplake Wood LWS and immediately adjacent to the Warren Wood LWS. Other LWSs and potential LWSs are within 2km of SG65.

Other protected/notable species include numerous records of mammal, bird, amphibian, plant and invertebrate.

There may be potential to secure improvement to surface water quality.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site boundary is approximately 1.5km away from the AONB but site is not visible. No adverse impact on AONB anticipated.

The northern part of the site (SG-65) will result in loss of characteristic features of low-lying farmland, hedgerows, lines of trees and ditches. The southern part comprises an arable field and will come close (approximately 30m) to Sonning Eye conservation area.

The site will be viewed in the context of quarrying in wider area and adjacent to the site which reduces the site’s sensitivity in landscape character and visual terms. Restoration of the site once worked has the potential to deliver landscape enhancements in the long term.

The Thames Path National Trail is a short distance away from site with occasional views towards the site. Visual impacts (eg on users of the Thames Path) are considered to be moderate but mitigatable in parts during operation.

There may be potential views from the River Thames (eg from boats). Another short footpath can be found along Spring Lane, a short distance from the southern end of the southern site. The site unlikely to be visible from A4155. Appropriate screen planting and bunding that is in keeping with the local character be may required to mitigate visual impacts.

There are no known historic landscape constraints.

Southern end of SG-11 is close to Sonning Eye conservation area and a sufficient stand-off to the settlement is likely to be required.

Overall the landscape and visual impact of the site allocation is considered to be low due to the site being an extension to an existing quarry which reduces the site’s landscape and visual sensitivity.

Site Restoration has the potential to deliver landscape enhancements in the long term.

Compliance with Policy C10: Transport - Highways Officer Assessment

Playhatch Road is known to have capacity issues in the peaks. Mitigation may be required to the roundabout junction to the west and due to the width of the road width and its current condition.

It is proposed that the minerals will be processed at the existing plant site at the Sonning works. Minerals will be transported from the extraction area to the works using a conveyor which has been approved via the Phase C planning consent, with two conveyor bridges over Spring Lane and Playhatch Road.

The existing access onto the B478 (Playhatch Road) considered acceptable in principle.

Conclusion

In line with the Core Strategy, the requirement for additional sites for sharp sand and gravel should be met primarily in the southern part of the County particularly over the first half of the pan period. As the Caversham Quarry has an extant consent for mineral working (MW.0158/11) with extraction of minerals to cease by 31.12.2027, it will contribute to meeting Oxfordshire’s need’s over the Local Plan period not least as most of the reserve has yet to be worked. Restoration of the Quarry is required by 31.12.2029.

Given the long history of mineral working in this area, the proposed extension to the Quarry is considered suitable for allocation, subject to appropriate mitigation, including a potential buffer to mitigate impact on Sonning Conservation Area and the amenity of local residents. However, careful consideration will be required to the phasing of works to avoid any potential adverse cumulative impacts arising from the existing works at Caversham Quarry and the works at proposed site proceeding concurrently, particularly in relation to highway impacts. It is likely that the additional capacity proposed at this site would need to be phased to come forward towards the latter part of the Plan Period. There may therefore be only limited scope for mineral working early in the Plan period.

Site SG-17: Land at Culham

Site Information (as nominated in 2018) Site Location Land at Culham

Grid Reference SU 537 945

Administrative Area South Oxfordshire

Parish Clifton Hampden, Sutton Courtenay

Site Nominee(s) Hills Quarry Products Ltd

Proposed Development Sharp sand and gravel extraction. Potential new quarry.

Site Area 104ha ha Estimated annual 200,000 tpa output Estimated Reserves Estimated yield of 2.5 million tonnes (including depth/ Estimated working depth of up to 5.0m overburden) Estimated overburden of 1.29m

Proposed Restoration Agriculture / reed/marsh wet woodland areas / lakes and low land meadow/ biodiversity of habitat Access Access onto A415 Estimated Unknown Traffic Movements Year of Unknown Commencement Lifetime of 12.5 Years Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Thame Valley – Oxford to Strategy – Strategic Resource Cholsey) in the southern part of the county (South Oxfordshire). Areas (Policy M3) • Site is proposed as a potential new quarry. • Estimated yield of 4.0 mts. District Local Plan Allocation • The site lie within the safeguarded area for the new Thames River Crossing (as per Policy Trans3 of the emerging South Oxfordshire Local Plan and Core Policy 18 of the adopted Vale of White Horse Local Plan Part 1). • The proposed site is to the south east of Land Adjacent to Culham Science Centre which is proposed for residential development of approximately 3,500 homes by the South Oxfordshire Local Plan 2011-2034 Policy STRAT9: Land Adjacent to Culham Science Centre. • Biodiversity and Geodiversity • Site lies 2.3km to the north west of Little Wittenham SAC and Culham Brake SSSI. (Policy C7) • Ancient woodland (0.3ha) lies adjacent to south western corner of the site. • Radley Gravel Pits Extension (Proposed Local Wildlife Extension) lies 2.1km to the north of the site. • Site located in excess of 5km from a SINC or LNR or NNR. • Natural England advise the site supports a priority habitat (Deciduous woodland). Landscape / Visual (Policy C8) • Site lies within 1.5km of North Wessex Downs AONB. Water Environment and Flooding • Site does not lie within a Source Protection Zone. (Policy C3 and Policy C4)) • Site lies within Flood Zone 2 and 3. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies primarily over Grade 2 agricultural land which is centrally located, fringed by Grade 4 agricultural land. Historic Environment (Policy C9) • Site contains a Scheduled Monument (round barrow cemetery at Fullamoor Plantation) as confirmed by Historic England. • Historic England advise that archaeological remains on this site are dependent on water acting as a preservative, meaning that it is considered unlikely that this site is deliverable. Furthermore, Historic England advise it is quite possible that the archaeological interest of the site extends beyond the scheduled area, and the setting of the Monument needs to be conserved and the dewatering potentially needed to extract minerals could lead to the deterioration and/or loss of waterlogged deposits.

© Adams Hendry Consulting Ltd. 398 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Historic England conclude the likely impact of mineral working at this site would therefore appear likely to be unacceptable. • Settlement Site SE of Church lies 100m south of the site and Settlement Site N of Thames lies 300m west of the site (Scheduled Monuments). • Nuneham Courtenay (Grade I listed Park and Garden) lies 1.3km north of the site. • Fullamoor Farmhouse (Grade II Listed) lies 150m north of the site. Listed buildings at Appleford and Clifton Hampden lie 220m from the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • The site is considered to contain nationally important archaeological deposits. It contains part of a scheduled monument (SM 1421606). There are also several settlement sites on the south west side of the allocation. These have been identified as Cropmarks and appear to include several Romano British farmsteads as well as a number of linear features. Transport and Access (Policy • Site lies within 250m of the Oxfordshire Lorry Route Network (A415). C10) • The site is located adjacent to the River Thames with potential to enable the transport of minerals by water. • Areas of AM and PM peak traffic congestion identified in close proximity to the site. • Site does not lie within close proximity to areas with history of RTIs. Public Rights of Way (Policy C11) • Site lies adjacent to Thames Path. • Public footpath crosses through the site. Health and Amenity (Policy C5) • A residential dwelling lies approximately 25m north of the site. • Dwellings off Abingdon Road lie 150m north of the site. • Dwellings at Appleford and Clifton Hampden lie 220m from the site and dwellings at Long Wittenham lie 500m south east of the site. Green Belt (Policy C12) • Site lies within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within Dalton Barracks buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of three existing waste sites: Didcot Strategic STW, Culham JET and Sutton Courtenay. (minerals and waste sites) • Site lies within 3km of one existing minerals site: Sutton Courtenay Quarry (Bridge Farm). • Site lies within 3km of five nominated waste sites: 010 Sutton Courtenay Landfill (1,2&3), 217 Culham No.4 Site, 234 Didcot STW, 248 Thrupp Lane Radley and 290 Culham Science Centre. • Site lies within 3km of two nominated minerals sites: PFA-01 Land at Thrupp Lane, Radley and SG-62 Appleford.

Conclusion

This would be a new quarry within the Mineral Strategic Resource area and the Green Belt.

© Adams Hendry Consulting Ltd. 399 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Part of the site may be unworkable as the land is safeguarded for transport infrastructure in the emerging South Oxfordshire Local Plan and due to the presence of a Schedule Ancient Monument. The site is also primarily Grade 2 Best and Most Versatile Agricultural Land.

However, as a large site, the site is considered to have some potential for mineral extraction and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Application MW.0039/16 for sand and gravel extraction from the same site was refused on 30.11.2017 on a number of grounds including: i) Severe highway impacts, contributing to congestion, disruption and delays on the road network and associated air quality emissions. ii) The development would prejudice the future development of a new link road and Thames crossing along one of the routes safeguarded by policy TRANS3 of the emerging South Oxfordshire Local Plan 2033 and core policy 18 of the adopted Vale of White Horse Local Plan 2031 Part 1; and iii) the development would be inappropriate in the Green Belt and no very special circumstances exist to justify making an exception to National and Local Planning Policies.

A revised planning application MW.0074/18 for sand and gravel extraction from the same site was considered by the Council’s Planning and Regulation Committee on 15.07.2019, when the Committee resolved that permission be refused for the following reasons: i) Severe highway impacts, contributing to congestion, disruption and delays on the road network and associated air quality emissions ii) The less than substantial harm caused to the setting of, and therefore the significance of, the Grade II Listed Fullamoor Farmhouse would not be outweighed by the public benefits of the proposal. iii) The development is inappropriate in the Green Belt and no very special circumstances exist to justify making an exception to these policies.

The refusal notice will not be issued until after 22.07.2019, when the consultation period for amendments to the application closes.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records available on site indicate clayey sand and gravel with high levels of fines, although this decreases in depth where gravel becomes more prominent at around 2.5-3m bgl. Fair

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Irreplaceable Habitats within and adjacent to the site include records of ancient woodland adjacent to south-western corner of site. Records also exist of Notable Habitats including several areas of woodland within site. The site is in close proximity to the River Thames. Ponds are also likely to be within site and adjacent to it.

Records of European protected species include Great Crested Newt and several bat species. Other protected and notable species include numerous records of mammal, bird, amphibian, plant and invertebrate.

Local Designations Haywards Eyot LWS approx 350m to south and Clifton Hampden Meadows LWS approx 830m to the north-east. Other LWSs within 2km. Thames Clifton to Shillingford CTA 600m to east.

The site borders the Thames Path and therefore there may be longer term improvements in habitat and accessible green space if the site is worked and restored.

A number of potential key biodiversity constraints exist, including the immediately adjacent ancient woodland. The site is in close proximity to the Little Wittenham SAC, which is designated due to the population of Great Crested Newt present.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Views from the AONB (eg Wittenham Clumps) might be possible but distant and in context of other developments in the wider area.

The site is next to the River Thames which predominantly consists of intensively farmed arable fields with some pasture closer to the river. Mineral working will introduce intrusive development into a currently rural landscape.

Development has the potential to affect small woodland copses, hedgerow boundaries and rows of tree which are characteristic features in the landscape. Restoration however offers opportunities for landscape enhancements in the long-term.

The site adjacent to Thames Path National Trail and crossed by another PRoW. Level of visual impacts are anticipated dependent on phasing and transport route as HGV movements will add to landscape and visual impacts. Appropriate screen planting/ bunding can assist in mitigating effects on views but unlikely to be fully successful.

No known historic landscape constraints.

Overall the landscape and visual effects are considered to be moderate due to the impact on characteristic landscape features such as woodland copses, the proximity of Clifton Hampden conservation area and the impact on sensitive visual receptors such as users of the Thames Path, long-distance path and the River Thames.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site lie within the safeguarded area for the new Thames River Crossing (as per Policy Trans3 of the emerging South Oxfordshire Local Plan and Core Policy 18 of the adopted Vale of White Horse Local Plan Part 1). This infrastructure has recently received Housing and Infrastructure Funding (HIF) to help deliver the crossing. Although the exact alignment of this crossing is to be confirmed, one of the potential routes is through this site. Any extractions in this area should not compromise the timely delivery of this infrastructure.

© Adams Hendry Consulting Ltd. 402 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 In the absence of HIF infrastructure, such as new river crossing and Clifton Hampden by-pass, development generating new peak hour movements are being resisted by OCC given the severe road capacity and congestion issues in this local area. Any additional traffic on the lorry route is therefore likely to be resisted by OCC highways.

A new access onto A415 will need to provided to appropriate DMRB sightlines and vehicle turning facilities to deter obstructions along the A415.

Conclusion

In line with the Core Strategy, the requirement for additional sites for sharp sand and gravel should be met primarily in the southern part of the County particularly over the first half of the pan period. However, the priority of the Core Strategy is for the extension of existing quarries, where environmentally acceptable, before working new sites.

It is judged that the site is unlikely to meet all of the criteria as set out in Policy M4 in particular in respect of the highway network which has severe capacity and congestion issues, and potential adverse impacts on designed heritage assets.

The allocation of the site may threaten the strategy in the emerging South Oxfordshire Local Plan 2011-2034 which was submitted for Examination in March 2019 in particular if works were to progress prior to the Thames River crossing being in place to help address existing capacity issues on the highway network around Didcot. Furthermore, residential amenity of future residents of Land Adjacent to Culham Science Centre would need to be protected.

The site has other constraints including a scheduled monument on the western edge of the site and the majority of the site being located in flood zones 2 or 3. The site is also entirely within in the Oxford Green Belt. Mineral extraction is not inappropriate in the Green Belt, provided it preserves openness and does not conflict with the purpose of including land within. However exceptional circumstances for the release of the site for mineral working would need to be justified.

On this basis, the site should not be allocated in the Local Plan unless other considerations clearly outweigh the harm to the Green Belt.

Site SG-18: Land near Standlake

Site Information (as nominated in 2018) Site Location Land near Standlake Grid Reference SP401023 Administrative Area West Oxfordshire Parish Standlake and Northmoor

Site Nominee(s) Hanson Aggregates

Proposed Development Sharp sand and gravel extraction. Potential extension to Stanton Harcourt Quarry. Site Area 13 ha

Estimated annual Unknown output Estimated Reserves Estimated total yield of 0.5 mts (including depth/ Estimated working depth of 3.80m Estimated overburden of 1.17m overburden) Proposed Restoration Open & closed water habitats with potential for recreational after uses e.g. fishing. All Hanson operation use progressive restoration techniques. Access As existing through Stanton quarry – mineral taken by conveyor/jet pump. Estimated As existing Stanton quarry – legal Traffic agreement to route lorries away from settlements and through Dix Pit Movements Year of 2024 Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in the northern part of the county (West Oxfordshire). Areas (Policy M3) • Site proposed as a potential extension to Stanton Harcourt Quarry. • Estimated site yield is 0.5 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Cothill Fern SAC lies approximately 5.7km to the east south east of the site. (Policy C7) • Ancient Woodland lies 330m to the east of the site. • Site lies 935m from Langley’s Lane Meadow (SSSI), southwest of the site. • Dunster Meadow LWS is approximately 180m to west. Standlake Common LWS approximately 900m to south-west and other LWSs and pLWSs within 2km • New bridge Fish Pass Project (Priority Habitat and Restoration) lies 120m south of the site. • Dix Pit Extension (Proposed Local Wildlife Site Extension) lies 1.9km north of the site. • A Local Geological Site (Devil Quoits) lies 2.4km north of the site. • Natural England advise that this site supports coastal floodplain grazing marsh. Landscape / Visual (Policy C8) • Site lies in excess of 3km of any AONB. Water Environment and Flooding • Site overlies Flood Zones 2 and 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of Grade 4 agricultural land with a small area (approximately 20%) of Grade 3 agricultural land to the west of the site. Historic Environment (Policy C9) • Newbridge Mill, Grade II Listed, is located within 200m of the site to the south. • The High Street in Standlake is located approximately 700m to the northwest of the site, where there are numerous listed buildings. • Scheduled Monuments lie 800m to the west of the site and 560m to the east of the site. • Hinton Manor (Grade II listed Park and Garden) lies 3.8km to the south west of the site. • Site lies in excess of 5km from any battlefields or World Heritage Sites. • Site falls within an area identified by Historic England as being of high archaeological significance and requiring physical preservation (Oxfordshire Aggregates and Archaeology Assessment). Transport and Access (Policy • Site lies adjacent to the A415, which is a ‘local access route’ on the Oxfordshire Lorry Route. C10) • It is proposed that the mineral would be taken by conveyor/jet pump through the existing Stanton quarry.

© Adams Hendry Consulting Ltd. 406 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • There is a single ‘serious’ RTI history 1.5km northwest of the site. • Site traffic is likely to impact on AM and PM congestion on the A415. Public Rights of Way (Policy C11) • There are no PRoW through or adjacent to this site. Health and Amenity (Policy C5) • There is a residential property approximately 20m west of the site and 2 dwellings 150m to the south. • Residential properties on the edge of Standlake lie approximately 315m from the northwest boundary of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site fall within the RAF Brize Norton and Dalton Barracks Aerodrome Safeguarding areas. M10)

Potential Cumulative Impact • Site lies within 3km of 4 existing waste sites: Lakeside Industrial Park, Dix Pit (Sheehans), Dix Pit and Rear of (minerals and waste sites) Cemex Batching Plant Hardwick. • Site lies within 3km of one existing minerals site: Stanton Harcourt Quarry (Stonehenge Farm). • Site lies within 3km of 3 nominated waste sites: 003 Dix Pit, 103 Land at Lakeside Ind Est and 236 Sheehan Recycled Aggregates. • Site lies within 3km of 1 nominated minerals site: SG-27 Vicarage Pit.

Conclusion

The site lies within a Mineral Strategic Resource Area and is proposed as a potential extension to Stanton Harcourt Quarry. It lies adjacent to the A415, which is on the Oxfordshire lorry route network. It is proposed that the mineral would be taken by conveyor/jet pump through the existing Stanton quarry.

National Grid noted that the site crossed or is in close proximity to National Grid infrastructure. Natural England commented that this site supports coastal floodplain grazing marsh. The site also lies within a rich archaeological landscape and there are residential properties in close proximity to the site.

Subject to appropriate mitigation for any amenity impacts and to protect archaeological assets, the site is considered to have potential for mineral extraction given its location in the MSRA and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

PLANNING HISTORY

The existing Stanton Harcourt Quarry and Stonehenge Farm sites are located to the west of the nominated site. Stanton Harcourt Quarry reserves are virtually worked out but operations have been extended through the permission for Stonehenge Farm.

Permission for working at Stonehenge Farm, with mineral being taken by conveyor to Stanton Harcourt Quarry, was originally granted on appeal 08.10.2010 (MW.0159/09 – APP/U3100/A/09/2107573) but subsequently varied.

The currently active permission for mineral working Stonehenge Farm is MW.0134/19 was permitted 07.02.2019. A variation of conditions is attached to consent APP/U3100/A/09/2107573 for the extraction of sand and gravel with associated processing plant, silt ponds, conveyors and ancillary works. Restoration to wetland/reed bed and fishing, extraction of basal clay to form hydrological seals and for the purpose of restoration on site.

Conditions require: • Extraction of minerals shall cease by 31.12.2023; • Restoration shall be completed by 31.12.2024; • Vehicular access to the site shall only be via the site access to Stanton Harcourt Quarry; • No mineral shall leave the extraction area except via the pipeline permitted by MW.0132/16.

Permission for revised method of transport of mineral from Stonehenge Farm site to plant site at Stanton Harcourt Quarry: MW.0132/16, permitted 12.06.2017: Installation and use of pipe system and associated pumps to transport minerals from the Stonehenge Farm extension area to the processing plant at Linch Hill permitted under appeal ref: APP/U3100/A/09/2107573. Condition requires: • Pipelines and all associated pumps, plant and machinery to be removed and site restored by 31.12.2024.

Stonehenge Farm has a permitted sand and gravel reserve of 1.55 mt which is proposed to be worked at a rate of up to 300,000 tpa. The permission has been commenced but no significant mineral extraction has yet taken place.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on the north east boundary of the site show relatively large deposits of very dense gravel, fine to medium grading in the upper tiers becoming coarser in depth. Overburden comprising silt and clay is limited in depth. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Records of Notable Habitats include several areas of woodland and waterbodies within vicinity of the site. There is a watercourse along eastern boundary.

European protected species include records for Great Crested Newt and bats. Records for protected and notable species including mammal, bird, amphibian, plant and invertebrates, including records within and adjacent to site.

A number of potential key biodiversity constraints exist, including the adjacent waterbodies, a watercourse and several areas of woodland, including an ancient woodland. The site is in close proximity to the Dunster Meadow LWS, is within the Lower Windrush Valley CTA and in close proximity to the Upper Thames CTA. There may be potential for habitat improvements towards the aims of Lower Windrush Valley Project.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This is a relatively small new site on the northern side of A415 comprising two medium-sized fields bounded by hedgerows. The site is located in the surrounding context of sewage treatment works (northeast), River Windrush (southeast), intensive agricultural fields (northwest) and restored gravel pits (southwest) which are now used for recreational purposes. Lower Windrush and associated vegetation forms important feature in the landscape and might be affected by development.

The site is approximately 300m from the edge of Standlake.

The site may not be perceived as extension but as new site in landscape and visual terms as it is separated from other former quarries by A415.

There are no PRoWs on site or adjacent to site. Views from more distant PRoWs might exist but are likely to be mitigatable. There may be occasional views from the country lane to the north of site and from the A415.

No known historic landscape constraints.

Despite the low effect on views the overall landscape and visual impact is considered to be moderate due to the nomination being considered a new site North of the A415. The site will extend into a rural area that is currently not subjected to such intrusive uses.

Compliance with Policy C10: Transport - Highways Officer Assessment

HGVs would be routed through Dix Pit to the B4449 (a Freight Priority Network - Tertiary) at Stanton Harcourt, then 7.3km to the A40. Products would be sent by conveyor or pipeline to Stanton Harcourt Quarry, then on from there by HGV

There have however been major problems with HGVs passing through Sutton village on B4449, although not all HGVs will go this way. A routing agreement is likely to be required.

The existing access is considered good.

Conclusion

This area has a long history of mineral working, with the extant consent granted for mineral working (on appeal) to the west of the site at Stonehenge Farm in 2019 to be worked by the end of 2023, with the site restored by the end of 2024.

The nominated site is to the east of Stonehenge Farm, and albeit that is located to the north of the A415, the presence of mineral extraction at Stonehenge will change the landscape character of the area north of the A415 over the next few years.

Mineral workings at the nominated site, is proposed to use the existing access to Stanton Quarry with minerals transported via Stanton Quarry by conveyor or jet pump and then by road in accordance with the existing lorry routing agreement in place for Stanton Quarry.

Mitigation will be required as this area is identified by Historic England as being of high archaeological significance and requiring physical preservation (Oxfordshire Aggregates and Archaeology Assessment). Measures to protect residential amenity must also be in place.

However, the site is considered suitable for allocation within the Sites Plan, with works to be phased after 2023 (assuming that mineral extraction will have ceased by that date at Stonhenge Farm) to avoid any adverse cumulative impacts. Restoration of the site must contribute to meeting the aims and objectives of the Lower Windrush Project area.

Site SG-20: Land between Eynsham & Cassington

Site Information (as nominated in 2018) Site Location Land between Eynsham & Cassington Grid Reference SP 441103 Administrative Area West Oxfordshire Parish Cassington, Eynsham, Hanborough Site Nominee(s) Oxford Aggregates - a collaboration between Hanson Aggregates & Smith & Sons (Bletchington) Ltd Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 37ha Estimated annual Unknown output Estimated Reserves Estimated total yield of 1.5 mts (including depth/ Estimated working depth of 4.5m Estimated overburden of 1-1.5m overburden) Proposed Restoration Potential to restore to a mix of agricultural land and/or a mosaic of wetland habitats including reedbed & wet woodland. Possible opportunity also for low key recreational / leisure use with improved public access (subject to land ownership). Access Access unconfirmed. Possible access from Cassington Road. Estimated Unknown Traffic Movements Year of Not before 2022 Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3. Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • The site is a potential new quarry. • Estimated total yield is 1.5mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. However, the site does lie in close proximity to the Cotswold Garden Village allocation, west of Lower Road. • West Oxfordshire DC have raised concerns regarding the relationship of these two sites, with particular emphasis on the potential impact on amenity; and also the potential impact of mineral working on the Siemens factory which needs to maintain a sterile environment for the construction of sensitive equipment. Biodiversity and Geodiversity • Oxford Meadows SAC lies approximately 1.3km to the east of the site. (Policy C7) • Wytham Woods SSSI lies 1.2km to the south east of the site and Cassington Meadows SSSI lies 1.3km to the east of the site. • Ancient Woodland (Wytham Great Wood) lies 1.2km to the south east of the site. • Wytham Park Proposed Local Wildlife Site lies 2.8km southeast of the site. • Site does not lie in close proximity to any LNRs or NNRs. Landscape / Visual (Policy C8) • Site lies in excess of 3km from any AONB. Water Environment and Flooding • Site is within Flood Zone 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 and Grade 4 agricultural land. Historic Environment (Policy C9) • Listed buildings 350m to the north of the site and 450m from the site in Eynsham and Cassington. • Eynsham Abbey (Scheduled Monument) lies 750m southwest of the site. • Yarnton Manor (Grade II listed Park and Garden) lies 2.8km northeast of the site. • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies 4.1km north of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 3.6km to the west of the site. • No known archaeological constraints. Transport and Access (Policy • Site crosses the A40, which is part of the Oxford lorry route network. C10)

© Adams Hendry Consulting Ltd. 413 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within close proximity to an area with a history of ‘serious’ RTI’s both west and east along the A40. • Site lies within an area likely to be impacted by AM and PM congestion (along the A40). Public Rights of Way (Policy C11) • There is a footpath which cuts through the centre of the northern section of the site between the A40 and Cassington Road. Health and Amenity (Policy C5) • Dwellings on Cassington Road 15m from southern boundary of site. • The site surrounds Eynsham Cricket Club. • Dwellings in Cassington 300m east of the site and dwellings in Eynsham 140m west of site. Green Belt (Policy C12) • Site is located within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport and Dalton Barracks Aerodrome Safeguarding areas. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Worton Farm and New Wintles Farm. (minerals and waste sites) • Site lies within 3km of one existing minerals site: Cassington Quarry. • Site lies within 3km of 2 nominated waste sites: 008 New Wintles Farm and 009 Worton Farm (Areas C & D). • Site lies within 3km of 5 nominated minerals sites: SG-08 Lower Road, Church Hanborough, SG-20a Wharf Farm, Cassington, SG-20b Land at Eynsham, SG-29 Sutton Farm, Sutton and SG-31 Land east of Sutton.

Conclusion

The site is nominated as a potential new quarry and is within the Green Belt. The site is fragmented providing potential working areas both north and south of the A40. There is no longer potential for the site to use existing processing plant site at Cassington Quarry as this has now gone and there is a short- term permission to extract the reserve from the area of the former plant site. . There may be issues in accessing the site from the A40 since Highways England have raised concerns for other sites which access the strategic road network (although Highways England have not commented on this site to date).

The site may therefore provide potential opportunity for mineral extraction however further consideration should be given to vehicle access. As the site is fragmented and straddles both the north and south areas of the A40, there is potential for either of these areas to be worked in isolation.

For the reasons outlined above the site should therefore be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

No relevant minerals or waste planning history on the nominated site.

The nearby Cassington Quarry (to the east of Cassington) has a long history of mineral working dating from 1986. Only a small reserve of sand and gravel remains permitted to be worked, within the former plant site area (S.73 Application MW.0158/15 permitted 16.01.2016). The rest of the mineral working area has been or is being restored; or is now in various waste management uses. Mineral working to be completed on this site by 31.12.2020; and the site to be restored by 31.12.2022.

Mineral site nominations SG-20a and SG-20b adjoin this nomination to the south and have been put forward for possible working in conjunction with this nominated area, possibly all through Cassington Quarry. Nominated site SG-08 is close by to the north of this nomination and has also been put forward for possible working through Cassington Quarry.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on site are limited to north of the A40. Samples indicate that sites northern and eastern areas contain higher quality material. Records within the western area of the site indicate gravel with clay content. Fair - Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

A Habitat Regulations Screening Assessment has been undertaken which concludes that for site SG-20 there is no hydrological connectivity with the SAC and the site is not therefore considered to result in LSEs on this European site through impacts on the water level and / or quality.

The River Eynsham runs adjacent to the north and west of the site.

Records for European protected species include Great Crested Newt and bats. Other protected and notable species include numerous records for mammal, bird, amphibian, plant and invertebrates.

The site is in close proximity to several LWSs, the closest being Cassington Gravel Pits South and Long Mead. Site is also adjacent to Oxford Meadows and Farmoor CTA. There may be scope of habitat improvement and potential improvement in surface water quality.

Right of way crosses site. There may be potential accessible green space improvements. The site is adjacent to land identified as a Greenspace Access Area.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The is a new large site that comprises flat small-medium sized open agricultural fields with mature hedgerows and trees on both sides of the A40, which is a very busy road. The site includes a drain and extends to the bank of the River Evenlode both of which have characteristic riverside vegetation and which might be affected. The nomination will surround Eynsham Cricket Club and will affect small number of properties and boundary vegetation.

Cassington Road is single track rural lane with no through traffic. The nomination will introduce large area of mineral working into a currently rural area. The A40, B4449 and nearby industrial uses reduce landscape sensitivity. Site restoration has the potential to deliver landscape enhancements in the long term.

The site is crossed by a footpath. Distant views from other footpaths in the vicinity of the site might also exist (eg Whytham Woods). There may also be occasional and glimpsed views from A40. Views from Cassington Road, which is single track rural lane also exist. The West Oxon LCA highlights the sensitivity of the landscape to mineral workings in views. Workings will substantially affect views but impact will be mitigatable in parts.

No known historic landscape constraints.

Overall the landscape and visual impact of this nomination is considered to be moderate but potential cumulative impacts will need to be considered should other nominated site in the vicinity be considered for allocation.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site straddles the A40. There is no longer an opportunity to use a conveyor or jet pump system to Cassington Quarry (former) plant site, as the Cassington processing plant has now been removed and the remaining reserve at the plant site is being extracted and processed through a mobile processing plant, with working to cease by 31st December 2020 MW.0158//150)

A new access off A40 is unlikely to be acceptable. The site may be accessed off Cassington Road having access via the B449 to the A40. Cassington Road would require an upgrade/widening if used as access route.

This is a large new site within the northern Oxfordshire rather than an extension and is located within the Green Belt. Works at the existing Cassington Quarry are due to cease in 2020 The use of the site for this mineral resource would therefore be likely to require planning permission for a new processing plant as the existing plant at Cassington Quarry has been removed. However, may be possible to use the existing purpose built grade separated access for Cassington quarry to the A40. A new access off A40 is unlikely to be acceptable to County Highways or Highways England. Works to Cassington Road may be required to make this acceptable for access.

The requirement for additional sand and gravel provision over the plan period is relatively small in northern Oxfordshire, there may be other potential options to meet sharp sand and gravel requirements within the Thames, Lower Windrush and Lower Evenlode Valleys area that may offer a more sustainable location for mineral working in accordance with Policy M4 of the Core Strategy. As the site is in the Green Belt, and is considered a new site, it is likely that development would not be considered to preserve the openness of the Green Belt, noting the landscape and visual sensitivity of the site.

SG-20a – Land between Eynsham & Cassington

Site Information (as nominated in 2018) Site Location Land between Eynsham & Cassington Grid Reference SP 449095 Administrative Area West Oxfordshire Parish Cassington Site Nominee(s) Oxford Aggregates - a collaboration between Hanson Aggregates & Smith & Sons (Bletchington) Ltd Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 78ha Estimated annual Max 450,000 tpa output Estimated Reserves Estimated total yield of 1.6 mts (including depth/ Estimated working depth of 4.5m Estimated overburden of Approx. 1 – 1.5m overburden) Proposed Restoration Potential to restore to a mix of agricultural land and/or a mosaic of wetland habitats including reedbed. Possible opportunity also for low key recreational / leisure use with improved public access (subject to land ownership). Access Purpose-built grade separated access to Cassington quarry off the A40. Estimated Traffic Vehicle movements as existing. Movements Year of From 2022 onwards Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3. Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • Potential new quarry. • Estimated total yield is 1.6 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • West Oxfordshire DC have raised concerns regarding the potential impact of mineral working on the Siemens factory which needs to maintain a sterile environment for the construction of sensitive equipment. Biodiversity and Geodiversity • Oxford Meadows SAC lies approximately 290m to the east of the site at its closest point. (Policy C7) • Wytham Woods SSSI lies 20m south east of the site (on the other side of the River Thames) and Cassington Meadows SSSI lies 290m to the east of the site. • Ancient Woodland (Wytham Great Wood) lies 65m to the south east of the site. • Wytham Park Proposed Local Wildlife Site lies 1.7km southeast of the site. • Kings Weir Fish Pass Project lies 2km east of the site (Priority Habitat Creation and Restoration). • Site does not lie in close proximity to any LNRs or NNRs. • The Berks, Bucks & Oxon Wildlife Trust have raised concerns that development at this site would lead to hydrological changes that might adversely affect the habitats in nearby LWSs (eg Somerford Mead LWS, which is designated for its rare Lowland Meadow habitat) and any designated sites downstream such as the Cassington Meadows SSSI and Pixey & Yarnton Mead SSSI/SAC. Landscape / Visual (Policy C8) • Site lies in excess of 3km from any AONB. Water Environment and Flooding • Site lies within Flood Zone 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Approximately 40% of the site is Grade 3 agricultural land with the remainder Grade 4. Historic Environment (Policy C9) • There are there are a number of listed buildings in Cassington, the closest being approximately 350m to the north of the site boundary. There also a number of listed buildings in Eynsham approximately 1km to the west of the site boundary. • Eynsham Abbey (Scheduled Monument) lies 1.6km west of the site. • Yarnton Manor (Grade II listed Park and Garden) lies 1.9km northeast of the site.

© Adams Hendry Consulting Ltd. 420 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies 4.6km north of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 4.5km to the west of the site. • Historic England have advised that the site lies within the setting of the Eynsham Conservation Area, and that the potential impact of this would need to be considered in determining what area, if any, of the sites is suitable for mineral extraction • The site is located in an area of considerable archaeological interest. A probably prehistoric enclosure has been identified from cropmarks within the site area. The site also contains the earthwork remains of Somerford deserted medieval village. Transport and Access (Policy • Site is within 1km of the A40 access, which is on the Oxfordshire lorry route network. C10) • Areas with potential traffic congestion lie at AM and PM peak times lie within close proximity along the A40. Public Rights of Way (Policy C11) • The site lies in close proximity the Thames Path and the Oxford Greenbelt Way, on the opposite side of the River Thames. Health and Amenity (Policy C5) • There are a small cluster of residential properties on the River Evenlode adjacent to the Site.

Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration opportunity. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport and Dalton Barracks Aerodrome Safeguarding M10) areas.

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Worton Farm, Charlett Tyre Yard and New Wintles Farm. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Cassington Quarry. • Site lies within 3km of 2 nominated waste sites: 008 New Wintles Farm and 009 Worton Farm (Areas C & D). • Site lies within 3km of 8 nominated minerals sites: SG-04 Land at Mead Farm, Yarnton, SG-05 Land to the East of Cassington Quarry, SG-08 Lower Road, Church Hanborough, SG-16 Land at Stonehouse Farm, Yarnton, SG-20 Land between Eynsham & Cassington, SG-20b Land at Eynsham, SG-29 Sutton Farm, Sutton and SG-31 Land east of Sutton.

Conclusion

The site is fragmented into east and western sections and separated by the Old Canal running north to south. The site overlies the River Evenlode which connects to the River Thames to the south as well as other minor watercourses.

The site is also in close proximity to the Oxford Meadows SAC and the potential for mineral working to give rise to significant adverse effects will be a key consideration going forward. Other key issues include impact on heritage assets and residential amenity.

Potential access to the site is via Cassington Road which runs adjacent along the site northern boundary and provides access to both the A40 and B4449,

The site is therefore considered to have some potential for mineral development and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no relevant minerals or waste planning history on the nominated site.

Cassington Quarry Plant Site (Hanson) S.73 Application MW.0158/15 permitted 16.01.2016 for continued mineral working and restoration with imported materials, to enable working of minerals from beneath plant site. Conditions require mineral working to be completed by 31.12.2020; and the site to be restored by 31.12.2022. Mineral working within this area has been commenced.

Mineral site nominations SG-20 and SG-20b adjoin this nomination to the north and west and have been put forward for possible working in conjunction with this nominated area, possibly all through Cassington Quarry. Nominated site SG-08 is close by, to the north of SG-20, and has also been put forward for possible working through Cassington Quarry.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource Borehole samples taken from the site area indicate a high level of fine to coarse gravel and medium to coarse sand with limited fine content under limited overburden. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Due to the close proximity and hydrological connectivity of the site to the Oxford Meadows SAC, the fact that dewatering may occur and the fact that historic minerals workings close to the SAC have resulted in drawdown of groundwater within parts of the site without mitigation, a conclusion of likely significant effects is drawn in the HRA Screening . If this site is selected for inclusion in the final plan an appropriate assessment will be required in which the effectiveness of mitigation measures (e.g. construction of a clay bund keyed into the underlying clay to create a hydraulic barrier, or prohibition on dewatering) will be investigated.

The River Evenlode is within the eastern parcel of the nominated site.

© Adams Hendry Consulting Ltd. 423 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Records for European protected species include Great Crested Newt and bats. Other protected and notable species include numerous records for mammal, bird, amphibian, plant and invertebrates.

The site is adjacent to Wytham Woods SSSI. Cassington Meadows and Wytham Ditches & Flushes SSSIs are within 1km. It is also close proximity to several LWSs, the closest being Cassington Gravel Pits South, Somerford Mead, Long Mead, Swinford Farm Meadow and Cassington to Yarnton Gravel Pits. The site is partly within Oxford Meadows and Farmoor CTA.

There is potential for habitat improvement, and the improvement in surface water quality, on the site’s restoration.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This proposed new large allocation seeks to introduce quarrying into an area that is characterised by agricultural fields with mature hedgerows and trees. The site extends to the bank of the River Thames, the River Evenlode and includes the Old Canal, all of which together with accompanying vegetation are important elements in the landscape.

The historic field pattern of smaller more irregular fields appears to have prevailed. Development is likely to impact on characteristic features such as mature vegetation, meadows.

The A40 is a detractor in northern part of the site, the southern part is perceived as tranquil.

Development will impact on views and the perception of PRoW users, and users of the River Thames. There may be occasional glimpsed views from Whytham Woods or other elevated ground and occasional views from Cassington Road which is rural lane. The West Oxon LCA highlights the sensitivity of the landscape to mineral workings in views.

No known historic landscape constraints.

Overall the landscape and visual impact of this nomination is considered to be substantial due to this being a new very large site (not an extension), which will introduce mineral workings into a rural tranquil area that is currently characterised by agriculture and floodplain vegetation. The allocation will also adversely affect sensitive views eg from the River Thames and the Thames Path.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site has good existing access direct on to A40 using the purpose built grade separated access to Cassington Quarry.

© Adams Hendry Consulting Ltd. 424 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 However, there is no longer an opportunity to use a conveyor or jet pump system to Cassington Quarry (former) plant site, as the Cassington processing plant has now been removed and the remaining reserve at the plant site is being extracted and processed through a mobile processing plant, with working to cease by 31st December 2020 MW.0158//150)

Conclusion

This is a large new site within the northern Oxfordshire rather than an extension and is located within the Green Belt. Works at the existing Cassington Quarry are due to cease in 2020. The use of the site for this mineral resource would therefore be likely to require planning permission for a new processing plant as the existing plant at Cassington Quarry has been removed. However, may be possible to use the existing purpose built grade separated access for Cassington quarry to the A40.

Given the proximity of the site to the Oxford Meadows SAC and other environmental constraints affecting the eastern parcel of the site nomination in particular, it is not recommended that this part of the site is allocated. The western parcel remains a sizeable area (32 ha) and with appropriate buffers and mitigation in place in particular to safeguard the River Thames and Evenlode, may offer potential to meet sharp sand and gravel requirements within the Thames, Lower Windrush and Lower Evenlode Valleys area. However, as the site is in the Green Belt, and arguably can be considered a new site, it is likely that development would not be considered to preserve the openness of the Green Belt, noting the landscape and visual sensitivity of the site.

SG-20b – Land between Eynsham & Cassington

Site Information (as nominated in 2018) Site Location Land between Eynsham & Cassington Grid Reference SP 445095 Administrative Area West Oxfordshire Parish Eynsham Site Nominee(s) Hanson Aggregates Proposed Development Sharp sand and gravel extraction. Potential new quarry or extension to Cassington Quarry. Site Area 41ha

Estimated annual Max 450,000 tpa output Estimated Reserves Estimated total yield of 1.86 mts (including depth/ Estimated working depth of 7-8m Estimated overburden of up to 0.8m overburden) Proposed Restoration Progressive restoration to form a series of reedbeds and small water. Access Access unconfirmed. Possible access from Cassington Road. Estimated Traffic Unknown Movements Year of Not before 2022. Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3. Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • Potential new quarry. • Estimated site yield is 1.86 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • West Oxfordshire DC have raised concerns regarding the potential impact of mineral working on the Siemens factory which needs to maintain a sterile environment for the construction of sensitive equipment. Biodiversity and Geodiversity • Oxford Meadows SAC lies approximately 1.5km to the east of the site. (Policy C7) • Site does not lie within or adjacent to ancient woodland. • Wytham Woods SSSI lies 320m south east of the site (on the other side of the River Thames) and Cassington Meadows SSSI lies 1.7km east of the site. • Ancient Woodland (Wytham Great Wood) lies 375m to the south east of the site. • Wytham Park Proposed Local Wildlife Site lies 2.1km southeast of the site. • Site does not lie in close proximity to any LNRs or NNRs. • The Berks, Bucks & Oxon Wildlife Trust have raised concerns that development at this site would lead to hydrological changes that might adversely affect the habitats in nearby LWSs (eg Somerford Mead LWS, which is designated for its rare Lowland Meadow habitat) and any designated sites downstream such as the Cassington Meadows SSSI and Pixey & Yarnton Mead SSSI/SAC. Landscape / Visual (Policy C8) • Site lies in excess of 3km from any AONB. Water Environment and Flooding • Site lies within Flood Zone 3. (Policy C3 and Policy C4)) • Site does not lie within a source protection zone. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Approximately 80% of the site is Grade 3 agricultural land, with the remainder Grade 4. Historic Environment (Policy C9) • There are a number of listed buildings in Eynsham, within 490m to the west of the Site. • Eynsham Abbey (Scheduled Monument) lies 600m west of the site. • Yarnton Manor (Grade II listed Park and Garden) lies 3.2km northeast of the site. • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies 4.5km north of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 4.3km to the west of the site.

© Adams Hendry Consulting Ltd. 428 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Historic England have advised that the site lies within the setting of the Eynsham Conservation Area, and that the potential impact of this would need to be considered in determining what area, if any, of the sites is suitable for mineral extraction. • The site is located in an area of archaeological interest. In the western part of the site limited evaluation has identified evidence of a late Bronze Age and early Iron Age settlement on a gravel island. Transport and Access (Policy • Site is within 700m of the A40 access to the north east via Cassington Road. C10) • Cassington Road is currently used to provide access to commercial units within Partridge Yard, which comprise businesses associated with the transport and haulage sector. • Areas with potential traffic congestion lie at AM and PM peak times lie within close proximity along the A40. • Poor access to public transport connections. Public Rights of Way (Policy C11) • Bridleway and footpath run adjacent to the site’s western boundary. Health and Amenity (Policy C5) • Eynsham Cricket Club is adjacent to the northern boundary of the Site. • Eynsham is within 250m of the western boundary of the Site. Green Belt (Policy C12) • Site within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport and Dalton Barracks Aerodrome Safeguarding areas. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Worton Farm and New Wintles Farm. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Cassington Quarry. • Site lies within 3km of two nominated waste sites: 008 New Wintles Farm and 009 Worton Farm (Areas C & D). • Site lies within 3km of 5 nominated minerals sites: SG-08 Lower Road, Church Hanborough, SG-20 and SG-20a Land between Eynsham & Cassington, SG-29 Sutton Farm and SG-31 Land East of Sutton.

Conclusion

The site lies within the Minerals Strategic Resource area and is a potential extension to Cassington Quarry. Potential access to the site is via Cassington Road which runs adjacent along the site northern boundary and provides access to both the A40 and B4449, north of which form part of the Oxfordshire Lorry route Network.

There are a number of sensitive receptors in the vicinity of the site, the potential impact on which will need further consideration.

The site is however considered to have some potential for mineral development and will be subject to further detailed assessment.

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no relevant minerals or waste planning history on the nominated site.

Mineral site nominations SG-20 and SG-20a adjoin this nomination to the north and west and have been put forward for possible working in conjunction with this nominated area, possibly all through Cassington Quarry. Nominated site SG-08 is close by, to the north of SG-20, and has also been put forward for possible working through Cassington Quarry.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on site demonstrate significant levels of sandy gravel beneath limited overburden. Grading of this material indicates improved quality with depth. Good.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

A Habitat Regulations Screening Assessment has been undertaken which concludes that for site SG-20 there is no hydrological connectivity with the SAC and the site is not therefore considered to result in likely significant effects s on this European site through impacts on the water level and / or quality.

The River Evenlode is a notable habitat adjacent to the site.

Records for European protected species include Great Crested Newt and bats. Other protected and Notable species include numerous records for mammal, bird, amphibian, plant and invertebrates.

The site is in close proximity to several LWSs, the closest being Cassington Gravel Pits South and Long Mead. Site partly within Oxford Meadows and Farmoor CTA.

There is potential for habitat improvement, and the improvement in surface water quality, on the site’s restoration.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This is a large new site that is characterised by flat open agricultural fields with mature hedgerows and trees on the Eastern side of Eynsham. The site is set in a wider landscape context of agricultural fields, urban fringe uses (eg allotments, business park and B4449) a short distance away to the south and east. Farmland is considered sensitive to development

A PRoW runs along the western boundary of the site. Footpaths represent important open space resource at the edge of Eynsham.

Development is expected to the visible from PRoWs slightly further afield and/or higher ground (eg Wytham Woods). Occasional views from Cassington Road. Visual impacts considered to be moderate.

No known historic landscape constraints.

The landscape and visual impact is considered to be substantial overall due to the large size of the site, the isolated nature of the allocation, the sensitivity of the local landscape to development and the proximity to Eynsham.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site is close to A40, although the access route is not confirmed. Cassington Road would require an upgrade/widening if used as the access route.

There is no longer an opportunity to use a conveyor or jet pump system to Cassington Quarry (former) plant site, as the Cassington processing plant has now been removed and the remaining reserve at the plant site is being extracted and processed through a mobile processing plant, with working to cease by 31st December 2020 MW.0158//150)

A new access onto Cassington Road, which would need improvement, would also be required. Use of the existing purpose built grade separated access for Cassington quarry to the A40 may be an option but would need further investigation.

The site’s proximity to the ecological receptors, the Siemans factory and residential development in Eynsham would also require mitigation.

Site SG-23 – Windrush North, Gill Mill

Site Information (as nominated in 2018) Site Location Windrush North, Gill Mill Grid Reference SP 361 079 Administrative Area West Oxfordshire Parish Ducklington Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Development Sharp sand and gravel extraction. Potential extension to Gill Mill Quarry. Site Area 11.5 ha Estimated annual Up to 400,000 tpa output Estimated Reserves Estimated total yield of 0.8 mts (including depth/ Estimated working depth of up to 6.0m overburden) Estimated overburden of up to 1.5m Proposed Restoration Progressive restoration continuing the current approved restoration scheme to a mix of new biodiverse habitats; reedbed, reedmarsh and wet woodland and to open water for amenity and public access use. Access Existing access onto the A415. Routing agreement to the A40. Estimated The extracted sand and gravel would Traffic be moved by conveyor or dumper to the existing permitted central primary Movements processing plant. As per the existing Gill Mill Quarry operation. Year of 2034 or earlier within the life of the Commencement current permitted development. Lifetime of Planning permission MW.0050/13 Operation provides for mineral extraction to 31st December 2040. Permitted reserves

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3. Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • Potential extension to an existing minerals site (Gill Mill Quarry). • Estimated total yield of 0.8 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. (Policy C7) • Site lies immediately adjacent to the Ducklington Mead SSSI to the south east as confirmed by Natural England. • Ancient Woodland lies 630m to the south of the site and Boys Wood lies 900m south of the site. • Site does not lie within close proximity to any LNRs, NNRs or Local Geological Sites. • Cokethorpe Park Proposed Local Wildlife Site lies 550m to the south of the site. • Natural England advise that likely potential impacts to the SSSI include changes in ground or surface water hydrology, air pollution from traffic and dust deposition. • Natural England and the Berkshire, Buckinghamshire and Oxfordshire Wildlife Trust (BBOWT) advise should this site be considered for inclusion in the plan, further detailed assessments (building on those undertaken for the existing quarry) would need to be undertaken to determine whether this site could be extracted whilst avoiding significant impacts (including cumulative impacts with the existing quarry) on the SSSI. Landscape / Visual (Policy C8) • Site lies in excess of 3km from any AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4) • There is a large area of Flood Zone 2 running through the centre of the Site, with a narrow area of Flood Zone 3 running along the east areas of the site. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • There are numerous Listed Buildings within 70m of the Site to the west at Ducklington. • Site lies in close proximity (30m) from the Ducklington Conservation Area.

© Adams Hendry Consulting Ltd. 436 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Two Scheduled Monuments lie 1km north of the site (Bishop of Winchester’s Palace and Medieval Manor remains). • Eynsham Hall (Grade II listed Park and Garden) lies 3.8km northeast of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Historic England advise the site appears to be within the setting of the Stanton Harcourt and Sutton Conservation Area, the potential impact on the setting of which should be taken into account in deciding whether or not this site, or part of it, is suitable for mineral extraction. • The site is located in an area of archaeological interest. The allocation is however covered by alluvial deposits which will have effectively masked any cropmark features or features.

Transport and Access (Policy • Site lies within 500m from the Oxfordshire Lorry Route Network (A415). C10) • Transport movements associated with the site are as per the existing Gill Mill Quarry operation and the site will use the existing access onto the A415 at the existing junction with a routing agreement to the A40. • There is a single ‘fatal’ RTI on the A415, within 1km of the Site. • AM and PM peak traffic congestion areas identified in close proximity to the site. Public Rights of Way (Policy C11) • There is a public footpath which runs from Ducklington through the centre of the Site and north towards Witney (Windrush Path). Health and Amenity (Policy C5) • Residential dwellings in Ducklington lie within 50m west of the site. • WODC also advise the area is well-used for recreational purposes – something that is likely to further increase as the East Witney Strategic Development Area (SDA) to the north/north-east is built out. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton Aerodrome Safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 4 existing waste sites: Witney STW, T&B Motors Witney, Gill Mill Quarry and Rear of Cemex (minerals and waste sites) Batching Plant Hardwick. • Site lies within 3km of 1 existing minerals site: Gill Mill Quarry. • Site lies within 3km of 3 nominated waste sites: 233 Witney STW, 249A High Cogges Farm and 249B High Cogges Farm. • Site lies within 3km of 2 nominated minerals sites: SG-27 Vicarage Pit and SG36 Friars Farm.

Conclusion

The site does not operate as an existing minerals site and is a potential extension to the existing site at Gill Mill Quarry. The site appears to be in use for agricultural purposes.

The site lies within 500m of the Oxfordshire Lorry Route Network (A415). Transport movements associated with the site are as per the existing Gill Mill Quarry operation and the site will potentially use the existing access onto the A415 at the existing junction with a routing agreement to the A40.

The site lies immediately adjacent to the Ducklington Mead SSSI. Further detailed assessments would need to be undertaken to determine whether extraction could take place whilst avoiding significant impacts on the SSSI in proximity to the site.

Consideration should also be provided to the Grade II listed buildings and residential dwellings which lie within 250m to the west of the site in Ducklington, sufficient stand-off distance is likely to be required which may impact viability due to a reduction in the workable area.

Notwithstanding these constraints, the site is considered to have some potential as a mineral working site for sharp sand and gravel and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no minerals or waste planning history on the nominated site.

Gill Mill Quarry adjoins to the east. The Gill Mill area was first granted permission for sand and gravel extraction in 1988. Over the years there has been various extensions. The most recent permission for mineral working – MW.0050/13 – provided a large extension to the quarry. This is the main currently operative permission.

Planning permission MW.0050/13, permitted 15/06/2015, for the extraction of sand, gravel and clay as an extension to the existing Gill Mill site with the retention of processing plant. Conditions require cessation of mineral extraction by 31.12.2040; and completion of restoration by 31.12.2044.

Application MW.0050/13 stated total reserves at Gill Mill Quarry (existing quarry plus extension) of 7.8 mt, to be worked at approximately 0.35 mtpa, giving a working life of 22 years. This would take the working life of the quarry beyond the end of the period of the Minerals & Waste Local Plan (31.12.2031) by some 3 years, to 2034.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records available from both the northern and southern areas of the site indicate extensive depths of coarse - medium sand and fine gravel with coarse fragments and limited fine content. There is also limited depths of overburden across site. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known Irreplaceable Habitats within or adjacent to the site. Records of Notable Habitats include floodplain grazing marsh onsite. The site is also adjacent woodland and waterbodies. The River Windrush along eastern and western boundaries.

European protected species include with records for Great Crested Newt and bats in the area. Records of other protected/notable species include numerous records of mammal, bird, amphibian, plant and invertebrates. There are also a number of records for Otter and Water Vole along the watercourse.

© Adams Hendry Consulting Ltd. 439 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Several LWSs and pLWSs within 2km of the site. The site is also within the Lower Windrush Valley CTA and Lower Windrush Valley Project area.

Potential for Habitat and accessible greenspace improvements.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This site is a large extension to Gill Mill quarry but might be perceived as new site in landscape and visual terms. The River Windrush and associated vegetation form important feature in the landscape which is characterised by meadows and grassland fields bounded by hedgerows and mature trees. This is an area of distinct character that is considered sensitive in landscape character terms with the southern part being more sensitive than the northern part due to greater distance to existing quarry.

Allocation site adjoins Ducklington Conservation Area boundary which extends to the River Windrush. The southern end of allocation still shows some historic fields and field boundaries.

A PRoW from Witney crosses the site in a north- southerly direction before turning west into Ducklington. The PRoW will be directly affected by development and will need redirecting. Occasional views from Ducklington conservation area an d adjacent roads are likely.

No known historic landscape constraints.

The landscape impact of the southern part this allocation is considered to be substantial due to the close proximity to Ducklington, the conservation area, the loss of historic field patterns and hedgerows, and the adverse impact on public views.

The northern part is considered less sensitive in landscape and visual terms due to the stronger influence of the existing quarry.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site has good existing access direct on to A415, 2.5km from A40, which does not pass through any villages.

There may be scope to transfer extracted minerals internally by conveyor to Gill Mill Quarry.

The site is a nominated as an extension to Gill Mill Quarry however the extant consent (MW.0050/13) would take the working life of the quarry beyond the end of the period of the Minerals & Waste Local Plan (31.12.2031) by some 3 years, to 2034. This site nomination, if allocated in the Sites Plan, would therefore not increase the sharp sand and gravel provision available for working within the plan period. There is a concentration of remaining permitted reserves within northern Oxfordshire.

Should additional capacity be required, the northern part of the site may be suitable for allocation.

Site SG-27: Vicarage Pit, Cogges Lane

Site Information (as nominated in 2009) Site Location Vicarage Pit, Cogges Lane

Grid Reference SP397058

Administrative Area West Oxfordshire

Parish South Leigh, Stanton Harcourt

Site Nominee(s) Smith & Sons (Bletchington) Ltd

Proposed Development Sharp sand and gravel extraction. Possible extension to Gill Mill Tar Farm or potential new quarry. Site Area 50ha Estimated annual Unknown output Estimated Reserves Estimated total yield of 1.6 mts (I&O (including depth/ 2018) Estimated working depth of between overburden) 2.5 and 6.5m Estimated overburden of 0.5 -1.5m Proposed Restoration Public access and improvement of river corridor. Progressive restoration is likely. Access Access onto B4449

Estimated Unknown Traffic Movements Year of Unknown Commencement Lifetime of Possible extension to Gill Mill Tar Operation Farm – 3 year reserve life.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3. Areas (Policy M3) • Site is located in the northern part of the county (West Oxfordshire). • Site proposed as either an extension to Gill Mill Quarry or as a potentially free standing new quarry. • Estimated total yield of 1.6mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies in excess of 5km from International / European designated sites. (Policy C7) • Tar Wood (Ancient Woodland) lies 700m north of the site. • Stanton Harcourt SSSI lies 1km southeast of the Site. • Dix Pit proposed Local Wildlife Extension site lies 350m to the southeast of the Site and Cokethorpe Park lies 1.5km west of the site. • Devils Quoits Local Geological Site lies 1km southeast of the site. • Church Mill Fish Pass (Priority Habitat Creation and Restoration) lies 1.7km to the south of the site. • Natural England advise that the site supports coastal floodplain grazing marsh. • Site does not lie in close proximity to any LNR’s or NNR’s. Landscape / Visual (Policy C8) • Site lies in excess of 3km from any AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • There is a narrow area to the west of the Site within Flood Zone 3. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of AQMA. Soil Resources (Policy C6) • Site predominantly within an area of Grade 2 agricultural land, with a small area of Grade 4 to the west. Historic Environment (Policy C9) • The Stanton Harcourt Conservation Area lies 300m to the east of the Site. • Beard Mill and Beard Mill Farmhouse (both Grade II Listed) lie adjacent to the south of the site. • The Old Vicarage (Grade II Listed) lies 100m east of the Site. • The Devil’s Quoits Scheduled Monument lies 1km southeast of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 4.2km north of the site. • Historic England advise that the site has been identified as being adjacent to an area which has produced a large amount of archaeological evidence. If this site is taken forward, an exclusion strip to preserve the significant archaeological remains in the south eastern section should be considered.

© Adams Hendry Consulting Ltd. 444 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site does not lie in close proximity to any battlefields or World Heritage Sites. Transport and Access (Policy • The site is on the Oxfordshire Lorry Route (located off the B4449 and lies 2.2km from the A415 C10) both of which are classified as a ‘local access route’). • There are no ‘serious’ or ‘fatal’ RTI histories within 3km of the Site. • Site traffic is likely to impact on AM and PM congestion along the A415 south of Standlake. Public Rights of Way (Policy C11) • There is a footpath which runs south from Cogges Lane via the Old Vicarage down to Eynsham Road, cutting through the far east corner of the Site. Health and Amenity (Policy C5) • There are residential properties adjacent to the western boundary of the site (Beard Mill Farmhouse) and 100m east of the Site (the Old Vicarage). • Residential properties on Cogges Lane lie 15m north of the site. • Residential dwellings at Stanton Harcourt also lie 350m east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton, London Oxford Airport and Dalton Barracks M10) Aerodrome Safeguarding areas.

Potential Cumulative Impact • Site lies within 3km of 5 existing waste sites: Lakeside Industrial Park, Rear of Cemex Batching Plant Hardwick, Dix (minerals and waste sites) Pit, Dix Pit (Sheehans) and Gill Mill Quarry. • Site lies within 3km of 2 existing minerals sites: Gill Mill Quarry and Stanton Harcourt Quarry (Stonehenge Farm). • Site lies within 3km of 3 nominated waste sites: 003 Dix Pit, 103 Land at Lakeside Industrial Estate and 236 Sheehan Recycled Aggregates. • Site lies within 3km of 8 nominated minerals sites: SG-18 Land near Standlake, SG-23 Windrush North, Gill Mill, SG-28 Guy Lakes North, SG-29 Sutton Farm, Sutton, SG-30 Home Farm, Brighthampton, SG-31 Land East of Sutton, SG-36 Land at Friars Farm and SG-14 Stonehenge Farm.

Conclusion

Site nominated in 2009 so it is not known if the site is still available.

Site lies within a Mineral Strategic Resource Area. The site is on the Oxfordshire Lorry Route (located off the B4449 and lies 2.2km from the A415 which are classified as a ‘local access route’).

The site has been identified as being adjacent to an area which has produced a large amount of archaeological evidence and there are residential properties in close proximity to the site. The site is predominately Grade 2 agricultural land. The site is also located in three separate aerodrome safeguarding areas. Potential cumulative impacts will need to be considered further.

Whilst constraints are present, given the size of the site it is considered to have potential for mineral extraction and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no relevant minerals or waste planning history on the nominated site, although a small part of it has been the subject of historic mineral working which is now a small lake.

Gill Mill Quarry is nearby, to the north west and could be reached from this site by off-highway haul road and/or conveyor. The Gill Mill area was first granted permission for sand and gravel extraction in 1988. Over the years there has been various extensions. The most recent permission for mineral working – MW.0050/13 – provided a large extension to the quarry. This is the main currently operative permission.

Planning permission MW.0050/13, permitted 15/06/2015, for the extraction of sand, gravel and clay as an extension to the existing Gill Mill site with the retention of processing plant, etc (see below for fuller detail). Conditions require cessation of mineral extraction by 31.12.2040; and completion of restoration by 31.12.2044.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records available from the north demonstrate high clay content and a limited amount of sand and gravel. Good.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Records of Notable Habitats include woodland and waterbodies adjacent and within site. Part of the site likely comprises floodplain grazing marsh. Records of European protected species include records for Great Crested Newt and bats.

Numerous records for protected and notable species include mammal, bird, amphibian, plant and invertebrates. There are a number of records for Otter and Water Vole along the watercourse.

Local Designations Site partly within Lower Windrush Valley CTA. Tar Wood LWS approximately 700m north and Dix Pit LWS and extension approximately 330m east. Other LWSs within 2km.

The site is partly within Lower Windrush Valley CTA in the Lower Windrush Valley Project area (habitat and accessible greenspace improvements). There may be the potential to fill a link in the Windrush Path. Link to ongoing LWVP support. Limited restoration proposals.

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors. The site is sensitively located adjacent to the Thames and records indicate numerous protected and notable species are within the area.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This site is characterised by medium-large arable and pasture fields. The northern part of site consists of smaller enclosed pasture with mature boundary vegetation including trees.

The site is set in a landscape context of a former gravel pit complex (now restored to wetland) to the south and west and intensive agricultural fields to the northeast. Cogges Lane is narrow single-track road with small number of residential properties. The area perceived as tranquil and remote. Restoration of the site has the potential to deliver long-term landscape enhancements especially in the southern part..

A short section of footpath can be found at the southeastern corner of site, crossing the site. Several PRoWs are in the surrounding area that terminate at Cogges Lane and B4449. There are views of the site from Cogges Lane and a small number of properties along Cogges Lane. Mitigation in form of bunding and planting will work towards reducing visual impacts.

No historical landscape constraints.

Overall the landscape and visual impacts are considered to be moderate due to the large size of the allocation, the perceived isolated nature of the development and the impact on landscape character and views. The northern western part of the site is more sensitive in landscape character terms.

Compliance with Policy C10: Transport - Highways Officer Assessment

Access to the site on to B4449 from the south-west corner of the site appears to be the best option. The junction appears to have adequate visibility, although there may not be sufficient space to incorporate right-turn filter lane. The B4449 connects to the A415 and onto the A40 (6.3km). A routing agreement would be required to avoid Sutton village, to the east on B4449.

The site was nominated in 2009. There has been no indication from the site operator as to whether this site is still available.

This site, if allocated in the Sites Plan as an extension to Gill Mill Quarry, would not increase the sharp sand and gravel provision available for working within the plan period.

If the site were to be worked as a new, free-standing quarry then it is unlikely to be the most sustainable option. Priority is to bring forward sites for sand and gravel extraction in southern Oxfordshire to ensure there is more equal spilt of production capacity between north and south; and policy M4 states the priority is for the extension of existing quarries before working new sites.

Other potential constraints, identified in the high level assessment, indicate that mitigation would be required, including measures to offset visual impacts, impacts on residential amenity and historic assets. Potential cumulative effects in combination with other existing and nominated sites in the vicinity would also need to be considered further should this site be allocated.

SG-29: Sutton Farm, Sutton

Site Information (as nominated in 2018) Site Location Sutton Farm, Sutton Grid Reference SP423 070 Administrative Area West Oxfordshire Parish Stanton Harcourt Site Nominee(s) Smith and Sons (Bletchington) Ltd Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 141ha Estimated annual output 250-400k tpa Estimated Reserves Estimated yield of 5.0 mts. (including depth/ Estimated working depth of 4.5-5.0m overburden) Estimated overburden of up to 1.5m Proposed Restoration Progressive restoration to a mixed restoration scheme similar to that approved for Gill Mill including the creation of a range of new biodiverse habitats; reedbed, reedmarsh and wet woodland. Opportunities for public access and open water for recreation can also be included. Access The site would require a new access on to the B4449 from the north west of the site with all routing to the north to the A40 via Eynsham. No traffic other than for local deliveries through Sutton on the B4449.

Estimated Traffic 100-160 movements per day. Movements The lorries would be 8 wheel rigid tippers carrying c 20 tonnes. Year of 2034 or earlier within the life Commencement of the current permitted development at Gill Mill. Lifetime of Operation Unknown

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Windrush & Evenlode Strategy – Strategic Resource Valleys) in accordance with Policy M3 in the northern Oxfordshire area and is adjacent to SG- Areas (Policy M3) 31. • Site is located in the northern part of the county (West Oxfordshire). • Site is proposed as a potential new quarry according to the 2018 site nomination information. • Estimated total yield iof 5.0 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • Development is proposed to come forward on the old airfield to the south of Stanton Harcourt Biodiversity and Geodiversity • Oxford Meadows SAC lies approximately 4.2km to the north east of the Site. (Policy C7) • Cothill Farm SAC lies approximately 6.2km to the south east of the site. • Ancient Woodland lies 1.3km west of the site (Tar Wood) and 1.5km east of the site (Strond Copse). • Wytham Woods SSSI lies 1.5km east of the site and Stanton Harcourt SSSI lies 1.5km south of the site. • Site does not lie within 1km of an NNR or LNR. • Pinkhill Backwater Creation Project (Priority Habitat Creation and Restoration) lies 760m to the east of the site. • Dix pit Proposed Local Wildlife Site Extension lies 1.5km south of the site. • Devils Quoits Local Geological Site lies 2km south of the site. Landscape / Visual (Policy C8) • Site does not lie within 3km of any AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Approximately half of the site lie within Flood Zone 2 and 3, covering the east and north areas with the remainder in Flood Zone 1 • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 2 agricultural land. Historic Environment (Policy C9) • Stanton Harcourt and Sutton Conservation Area lies within 200m of the southwest boundary of the site. • Listed buildings on Sutton Lane lie 150m southwest of the site. • There are a number of listed buildings in Sutton located 350m south of the site. • Scheduled Monuments lie 250m north of the site (Sites near Foxley Farm) and 1.7km north of the site (Eynsham Abbey). • The Devil’s Quoits Scheduled Monument lies 1.8km south of the site.

© Adams Hendry Consulting Ltd. 453 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Blenheim Palace (World Heritage Site and Grade I listed Park and Garden) lies 7.1km north of the site. • Eynsham Hall (Grade II listed Park and Garden) lies 3.4km north west of the site. • The site is located in an area of archaeological interest. In the western part of the allocation there are a number of cropmark features. There is also indication of historic quarrying. Transport and Access (Policy • The site appears to have access to the B4449 which is a local access route on the Oxfordshire C10) Lorry Route approximately 4.5km from the A40. • To the south of the site, the B4449 passes through the village of Sutton Green. • There are no ‘serious’ or ‘fatal’ RTI histories within 3km of the Site. • Site traffic may impact on AM and PM congestion along the A40 and Eynsham. Public Rights of Way (Policy C11) • There is a footpath which runs from Sutton northwards, cutting through the west side of the Site, where it meets the B4449 Eynsham Road. • There is a footpath which runs adjacent to the southern boundary and a second footpath adjacent to the east boundary. Health and Amenity (Policy C5) • Dwellings on Eynsham Road appear to be located just within the western boundary of the site. • There are residential properties adjacent to the southwest corner of the site at Sutton Green. • There are a number of dwelling on Sutton Lane between approximately 130m and 400m south of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the London Oxford Airport and Dalton Barracks Aerodrome Safeguarding M10) areas.

Cumulative Impact (minerals and • Site lies within 3km of 4 existing waste sites: Dix Pit, Dix Pit (Sheehans), Gill Mill Quarry and Rear of Cemex waste sites) Batching Plant Hardwick. • Site lies within 3km of 1 existing minerals site: Stanton Harcourt Quarry (Stonehenge Farm). • Site lies within 3km of 2 nominated waste sites: 003 Dix Pit and 236 Sheehan Recycled Aggregates. • Site lies within 3km of 8 nominated minerals sites: SG-08 Lower Road, Church Hanborough, SG-20 Land between Eynsham & Cassington, SG-20a Wharf Farm, Cassington, SG-20b Land at Eynsham, SG-27 Vicarage Pit, Cogges Lane, SG-28 Guy Lakes North, adj B4449, SG-31 Land east of Sutton and SG-36 Land at Friars Farm.

Conclusion

The site is proposed as a new quarry. It is located within the MSRA in the northern Oxfordshire area. The site would be accessed via a local access route and is approximately 4.5km to A40 strategic through route. The village of Sutton Green is located on the B4449 in close proximity to the site.

There are other constraints to mineral working including the site’s proximity to the conservation areas in Stanton Harcourt and Sutton Conservation Area, proximity to residential properties and Grade 2 BMV agricultural land. Potential Cumulative impacts would also need to be considered further.

However, given the size of the site there may be some potential for mineral working and therefore the site will be carried forward for further assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No mineral and waste planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Three borehole records running West to east across the site indicate higher clay content within the sand and gravel beds in west which improve in quality moving east towards the Thames. Records taken from the south east corner of the site indicate high levels of sand and gravel (up to 4.5m) with limited overburden (up to 0.6m). Fair – Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Notable Habitats within/adjacent There is a small areas of woodland within the site. The western boundary of the site is also in close proximity to River Thames.

Records of European protected species include Great Crested Newt, bats. Other protected and notable species include numerous records for protected and notable species of mammal, bird, amphibian, plant and invertebrates.

The Farmoor Reservoir LWS is approximately 900m to east. Swinford Farm Meadow LWS is approximately 1.2km to north-east. Oxford Meadows & Farmoor CTA is approximately 370m to east.

There is the potential for habitat improvements and the potential improvement to surface water quality.

Overall the potential ecological impacts of the proposals are likely to be high. The site is large and in close proximity to several sensitive ecological receptors.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This is a large new site that is characterised by intensive arable fields with hedgerows and/or trees. Limb Brook and associated vegetation forms northern boundary and feature in the landscape. Landscape character of the site itself is considered to be low but as the site is large and comes close to Sutton and Stanton Harcourt conservation area impacts are likely to be of moderate significance.

The site is crossed by a PRoW. Further PRoWs run along the southern and eastern boundary, and in close vicinity of the site with views into the site. Views are likely from Sutton with occasional views from B4449. The site is flat and open which is visually sensitive.

Views from Sutton.

Occasional views from B4449 likely.

No known historic landscape constraints.

Overall the landscape and visual impact of this new site is considered to be moderate due to the large size of the site, the introduction of mineral workings into an currently rural area, the loss of characteristic agricultural uses and boundary vegetation, the close proximity to Sutton conservation area and the moderate impact on views.

Compliance with Policy C10: Transport - Highways Officer Assessment

Site access will be on to the B4449, 4.5km to A40. A routing agreement would most likely be required to avoid Sutton village, to the south on B4449.

A new site access from north-west corner of the site on to the B4449 will be required. There may be an issue with visibility but access improvements are likely to be acceptable. There may not be sufficient space to incorporate right-turn filter lane.

Conclusion

The site is a new site and is located in the northern part of the County where the requirement for additional sand and gravel provision for the plan period is relatively small. There may therefore be other potential options, including extensions to existing sites, to meet sharp sand and gravel requirements within the Thames, Lower Windrush and Lower Evenlode Valleys area that may offer a more sustainable location for mineral working in accordance with Policy M4 of the Core Strategy.

The site is not however in the Green Belt. If additional capacity is required, then this site may be suitable for allocation with appropriate mitigation in place to safeguard the amenity of local residents, the conservation area and sensitive ecological receptors. The existing footpath would need to be diverted. There would also be the loss of Grade 2 agricultural land.

Site SG-42: Nuneham Courtenay

Site Information (as nominated in 2018) Site Location Nuneham Courtenay

Grid Reference SU 540 995

Administrative Area South Oxfordshire

Parish Nuneham Courtenay

Site Nominee(s) Nuneham Estate Ltd Proposed Development Sharp sand and gravel extraction. Potential new quarry. Site Area 75 ha Estimated annual Unknown output Estimated Reserves Total 2,400,000m3 of gravel and (including depth/ sand = 3,984,000 – 4,800,000t 3.2m depth overburden) 0.9m overburden

Proposed Restoration To be confirmed.

Access Existing access. New access could provided to the A4074. Estimated Unknown Traffic Movements Year of To be confirmed. Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Landscape / Visual (Policy C8) • Site lies over 3km from an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. • Approximately half of the site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site located within 1km of an AQMA. Soil Resources (Policy C6) • Site lies within an area of predominantly Grade 4 agricultural land with small pockets of Grade 3 agricultural land. • Restoration plans to be confirmed. Historic Environment (Policy C9) • Nuneham Courtenay Conservation Area and Registered Historic Grade I listed Park and Garden adjoins the southern boundary of the site. • Historic England have acknowledged that the site does not include the Nuneham Courtenay conservation area but advise that site should avoid these areas and consideration be paid to the setting of this asset. • Site lies within 350m of Grade II listed properties in Lower Radley to the west of the site. • 3 Listed properties lie 185m south of the site and 2 listed properties lie 40m north of the site.

© Adams Hendry Consulting Ltd. 460 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within 1.3km from a Scheduled Monument (Settlement Site) and within 2km from another Settlement Site to the west. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • The site is located in an area of archaeological interest. In the northern part are some cropmarks, albeit somewhat indistinct in terms of character. • The archaeological remains of the Roman pottery production site could be considered to be of very high significance and could appear to be demonstrably of equivalent significance to scheduled monuments and may need to be physically preserved.

Transport and Access (Policy • Existing access to the site may be suitable. C10) • There is potential site access to the A4074 Oxfordshire Lorry Route via Lower Farm Lane (approximately 400m). • There may be an opportunity to promote the sustainable movement of excavated material via the River Thames. • No AM or PM peak traffic congestion areas identified within proximity to site. Public Rights of Way (Policy C11) • Public footpath within the site and the Thames Path runs along the opposite bank of the River Thames. • Restoration proposed. Health and Amenity (Policy C5) • Residential dwellings adjacent to the north of the site at Lower Farm. • One residential dwelling lies 25m south of the site and another lies 150m south east of the site. Green Belt (Policy C12) • Site lies within the Green Belt. • Restoration proposed. Aerodrome Safeguarding (Policy • Site lies within the Dalton Barracks buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Culham JET, The Metal Yard Nuneham Courtenay and Oxford STW. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • Site lies within 3km of 3 nominated waste sites: Culham No.4 Site, Culham Science Centre and Thrupp Lane Radley. • Site lies within 3km of 2 nominated minerals sites: PFA-01 Land at Thrupp Lane, Radley and SG-41 North of Lower Radley.

Conclusion

A large Site, within the Green Belt and the Mineral Strategic Resource Area, situated between the A4074 to the east and the River Thames to the west. There may therefore be an opportunity to promote the sustainable movement of excavated material via waterways as well as the potential to provide direct access onto the Oxfordshire Lorry Route Network (A4074).

A public right of way runs intersects the site and, although the site does not overlay the Thames Path, the potential visual impact from this National Trail will

The site lies adjacent to residential properties to the north of the site. However, due to the scale of the site, there is sufficient potential to provide a suitable measure of stand-off between the operational working area and sensitive receptors.

For the above reasons, the site may have potential for mineral development and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No mineral and waste planning

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on site show sand and gravel deposits of up to 3.2m with limited fines content (0-6%). A record within the northern area of the site shows a much lesser extent of sand and gravel at 1.5m with a greater level of overburden. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no known Irreplaceable Habitats within or adjacent to the site. Notable Habitats within or adjacent to the site include numerous areas of woodland bounding site. River Thames located adjacent to the eastern site boundary.

European protected species include records for Great Crested Newt and bats. Other protected/Notable species inclue numerous records for protected and notable species of mammal, bird, amphibian, plant and invertebrates.

Lower Farm Bottom Hay Meadow LWS is within Site. Several other LWSs are within 2km of site. The site partly within Thames & Cherwell at Oxford CTA.

Overall the ecological interests of the site need to be fully investigated. The site is sensitively located adjacent to the Thames. Further assessment and impacts on non-statutory sites of nature conservation must be considered.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

This a large new site that adjoins Nuneham Courtney Parks & Gardens and Nuneham Courtney conservation area. The site is more sloping at southern end of site and is predominantly characterised by intensive arable and pasture. Its proximity to Oxford and to major roads and rail is notable reducing landscape sensitivity. Development is expected have moderate effect on landscape character. Restoration of the site has potential to deliver landscape enhancements in the long term.

Thames Path National Trail runs on other side of the river with views into the site. Another PRoW crosses the site at its northern end. The site will impact on views from River Thames (eg boats). There are limited views from nearby roads due to sloping topography. The northern part of the site is more visible in views from A4074. Glimpsed views from a limited number of properties may be likely.

Mitigation planting that is in keeping with the landscape character along eastern river bank could assist in mitigating impact on views from the Thames Path.

No known historic landscape constraints.

Overall the impact of this large extension is considered to be moderate due to the large size of the site, the close proximity to Nuneham Courtney conservation area and Historic Parks & Gardens and the moderate impact on sensitive visual receptors in particular users of the Thames Path National Trail and the River Thames.

Compliance with Policy C10: Transport - Highways Officer Assessment

Any new access to be taken from the A4074, will route trips onto a particularly sensitive part of the network, which includes the southern perimeter road and the Golden Balls roundabout. Should an application come forward on this site it would be expected to include mitigation such as contributions to the improvements at the Golden Balls Roundabout.

Conclusion

In line with the Core Strategy, the requirement for additional sites for sharp sand and gravel should be met primarily in the southern part of the County particularly over the first half of the pan period. Whilst this site may be suitable for allocation with appropriate mitigation in place to protect historic assets, mitigate visual and ecological impacts and protect residential amenity, there is a potential highway constraint to providing a new/improved access onto the A4074.

The site is also within in the Oxford Green Belt. Mineral extraction is not inappropriate in the Green Belt, provided they preserve its openness and do not conflict with the purpose of including land within. It is unlikely that exceptional circumstances for the release of the site for mineral working could be justified.

SG-60: White Cross Farm

Site Information (as nominated in 2019) Site Location White Cross Farm, Wallingford

Grid Reference SU 605 877

Administrative Area South Oxfordshire

Parish Cholsey

Site Nominee(s) London Rock Supplies Ltd Proposed Development Sharp sand and gravel extraction with proposed restoration to a marina. Site Area 19 ha Estimated annual 140,000tpa output Estimated Reserves 550,000t (including depth/ 4-5m depth (average) 0.9 – 3m overburden overburden) Proposed Restoration Marina and recreational riverside park.

Access Existing access onto Reading Road (A329).

Estimated Traffic Average of 56 HGV movements Movements per day (28 in and 28 out of the site).

Year of Late 2019 Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Area (Thames, Lower Thame Valley – Oxford to Strategy – Strategic Resource Cholsey) Areas (Policy M3) • The site lies within the southern part of the County (South Oxfordshire). • Site is proposed as a potential new quarry and appears to be currently in agricultural use. • Estimated yield is 550,000 tons. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Little Wittenham SAC/SSSI lies approximately 5.3km to the north west of the site. (Policy C7) • Marsh Wood Ancient Woodland lies 2.3km to the northeast of the site. • Site does not lie within 1km of SSSI, NNR. • Ewelme Watercress Beds LNR lies 4.8km northeast of the site. • Local wildlife site does not lie within 500m of the site. Knapps Wichelo Proposed Local Wildlife Site lies 4km south east of the site. Landscape / Visual (Policy C8) • The site is immediately adjacent to the Chilterns AONB boundary (Western bank of River Thames forms boundary). • Natural England advise that consideration will need to be given to inter -visibility between the site and the AONB. The Chiltern Conservation Board raise similar issues. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a principal and secondary aquifer. • Site lies within Flood Zone 2 and 3. Air Quality (Policy C5) • Site does not lie within close proximity to an AQMA. Soil Resources (Policy C6) • Site lies predominantly within Grade 4 agricultural land with a strip of Grade 2 BMV agricultural land on the eastern edge of the site. Historic Environment (Policy C9) • Site does not lie within in or in close proximity to conservation area. • The nearest Grade II listed buildings are located within 110m east of the site in Mongewell. • White Cross House (Grade II listed) lies 150m north of the site. • Grade II listed milestone on Reading Road lies adjacent to the western boundary. • Site is located within 1.5km of a Grade II listed park and garden (Fairmile Hospital). • Scheduled Monuments lie 1.1km north of the site (Saxon Town and Wallingford Town Walls). Wallingford Castle and Wallingford Bridge lie 1.3km north of the site. • A further Scheduled Monument (North Stoke henge and ring ditch site) lies 1.4km south of the site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Fairmile Hospital (Grade II listed Park and Garden) lies 1.3km south of the site. • Archaeological evaluation has established that archaeological features dating to the prehistoric

467 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 period survive in the north west part of the site. Transport and Access (Policy • Site is adjacent to A329 on the Oxfordshire Lorry Route. C10) • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies close to area with history of serious RTIs (2 on Nosworthy Way within 800m of site). Public Rights of Way (Policy C11) • Thames Path runs adjacent along the site’s eastern boundary. Health and Amenity (Policy C5) • Nearest residential dwelling lies approximately 70m to the south of the site. • A day nursery is located opposite the site on the A329 approximately 70m to the west. • Dwellings in Mongewell lie 90m to the east of the site. • The closest Residential properties in Winterbrook are approximately 110m to the north of the site. • A cluster of residential dwellings lies within 260m south of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within RAF Chalgrove buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 2 existing waste sites: Oakley Wood and Battle Farm Crowmarsh. (minerals and waste sites) • There is 1 existing minerals site within 3km of the site: New Barn Farm Cholsey. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site lies within the Mineral Strategic Resource Area. It is adjacent to the Chilterns AONB (on the opposite bank for the River Thames). The potential inter-visibility between the site and the AONB will need further detailed assessment.

There are further constraints on the site that will need to be further considered, including potential adverse impacts on the amenity on nearby residential properties, the day nursery opposite the site and the Thames Path.

Whilst constraints are present, given the size of the site it is considered to have potential for mineral extraction and should be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No mineral or waste planning history on this site but subject to a current planning application MW.0033/18 which has yet to be determined.

Application MW.0033/18 proposes the extraction of 550,000 tonnes of sand and gravel at 140,000 tpa, commencing in 2019; extraction is proposed to be completed in 2023 and restoration of the site to a marina development completed in 2024.

The application is currently subject to a request for further information prior to being determined. Until the further information is provided it is not possible to say when the application would be determined, but it is not likely to be before January 2020.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Extensive borehole records across the site indicate shallow deposits of sand and gravel in the south west of the site with deeper deposits in the north east of the site. Records show a higher sand content than gravel. Sand reportedly contains a high amount of fine clayey material in places. Fair.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

No known Irreplaceable Habitats within or adjacent to the site.

Floodplain grazing marsh is known to be present. The site is adjacent to River Thames. Deciduous woodland is immediately to south.

Record of European protected species include several records for bats within local area. Other protected and Notable species include numerous records of mammal, bird, amphibian, plant and invertebrate. Species of note include Water Vole, Otter and Badger.

The site is partially within Thames Goring to Wallingford CTA. There is a pond north of Cholsey Marsh LWS which is located approximately 1.2km to the south. Given the sites positioning within the Thames Goring to Wallingford CTA, restoration and site enhancements should be in line with the objectives of this CTA.

© Adams Hendry Consulting Ltd. 469 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Overall there are several potential ecological impacts which will need to be fully assessed and mitigated, including the loss of floodplain grazing marsh and impacts on the adjacent river. Recent surveys have however found no new evidence of protected species within the site (pers comms Louise Fox and Ted Bosworth of Windrush Ecology (30th May 2019).

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Mineral extraction and after-use as a marina will adversely impact on the Chilterns AONB. The North Wessex Downs AONB also only 1.5km away.

This is new site bounded by River Thames A329 and 4130 south of Wallingford. The site is characterised by grazing marsh and pasture fields with hedgerow boundaries and trees. The proposed after-use as a marina will result in a permanent impact on the local character and has the potential to affect the setting of Wallingford and Cholsey.

Thames Path National Trail runs inside eastern site boundary with views into the site. Mitigation planting and bunding might work towards mitigating the impact on views during extraction but will not be fully successful and will also be inappropriate in the long-term. The proposed after use as a marina will result in a permanent impact in views caused by the marina, the potential re-routing of the Thames Path, the increased activity within the site and on the river and potential lighting.

Views may also be possible from the A4130 (especially the bridge over the Thames), from a low number of selected properties and occasionally also from A329.

No known historic landscape constraints.

Overall the landscape and visual impact of this allocation is expected to be substantial due to permanent loss of characteristic features, the impact on the Chilterns AONB, the impact on high-sensitive users of the Thames Path and the River Thames, and adjacent roads, and the potential impact on the separation between settlements. Site has also potential to affect the setting of the North Wessex Downs AONB (eg through activity and lighting).

Compliance with Policy C10: Transport - Highways Officer Assessment

A329 and A4130 are considered in principle acceptable for lorry freight movement but additional HGV movements will need to be assessed due to the road width and condition. The roundabout junction will require assessment at peak times as there are known capacity issues in this area.

A new access onto A329 (Reading Road) will need to be provided to DMRB standards which will mean the loss of significant vegetation. Exit only access onto A4130 is located near to the roundabout and is considered a concern with additional HGV movements turning in this location.

It is noted that the current application proposed that during the mineral excavation phase access will be provided by a left in from Reading Road and left out onto Nosworthy Way. During the Marina operational phase the Reading Road T-junction access would be changed from a left in only to an all movement priority. This must be supported by a robust assessment.

Conclusion

This is a new site within the mineral strategic resource area in Southern Oxfordshire. Core Strategy Policy M4 states that the priority is for the extension of existing quarries in preference to new sites.

There are number of potentially significant constraints to mineral working including its potential impact on the setting of the Chiltern AONB, the impact on high-sensitive users of the Thames Path and the River Thames and potential impacts on the amenity of sensitive receptors in close proximity to the site (including a day nursery) which would need to be appropriately mitigated.

Whilst there is a requirement for additional sand and gravel provision in Southern Oxfordshire, to address the current imbalance in the distribution of production capacity within the County, there may be other potential options to meet sharp sand and gravel requirements within the Thames, Lower Thame Valley – Oxford to Cholsey area that may offer a more sustainable location for mineral working in accordance with Policy M4 of the Core Strategy.

SG-62: Appleford

Site Information (as nominated in 2009) Site Location Appleford, Didcot

Grid Reference SU 527 924

Administrative Area South Oxfordshire

Parish Appleford-On-Thames

Site Nominee(s) Hanson Aggregates

Proposed Development Sharp sand and gravel extraction. Potential extension to Sutton Courtenay Quarry. Site Area 20ha Estimated annual 330,000 tpa output Estimated Reserves Estimated total yield of1.1 mts (including depth/ Estimated working depth of 4.7m Estimated overburden of 0.9m on overburden) average Proposed Restoration Potential for agricultural and/or leisure use.

Access Potentially direct from A4130 Estimated Subject to crossing the railway, Traffic mineral taken by conveyor to Sutton processing plant, then transportation Movements arrangements as for existing Sutton Courtenay Quarry. Year of Unknown Commencement Lifetime of 3 years Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Thames, Lower Thame Valley – Oxford to Strategy – Strategic Resource Cholsey) in the southern part of the county (South Oxfordshire). Areas (Policy M3) • Site is proposed as a potential extension to Sutton Courtney Quarry. • Estimated total yield of 1.1 mts. District Local Plan Allocation • The site lies adjacent to Housing Allocation Policy area (H2) as saved from the Local Plan 2011. Outline planning permission at this site for 2,030 homes was granted in 2016. Biodiversity and Geodiversity • Little Wittenham SAC lies 3.6km east of the site. (Policy C7) • Little Wittenham SSSI lies 3.6km east of the site. • Ancient Woodland lies 300m east of the site. • The nearest Local Nature Reserve (Mowbray Fields) is within 3km south of the site. • Kelart’s Field Proposed Local Wildlife Site lies 2.5km west of the site. • The Berks, Bucks & Oxon Wildlife Trust advise that the proposed site will include a little community orchard that has recently received TOE2 funding. Landscape / Visual (Policy C8) • Site lies within 1.7km of the North Wessex Downs AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. • Site lies within Flood Zone 2 and 3. Air Quality (Policy C5) • Site not located within 1km of AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 2 BMV (60%) and Grade 4 agricultural land (40%). • Restoration proposed, but specific scheme not yet determined. Historic Environment (Policy C9) • Scheduled Monument (Settlement site SE of Church) adjoins northern boundary of site. • A further two Scheduled Monuments are within 2km north of the site. • Listed buildings in Appleford lie 700m north of the site and listed buildings in Didcot lie 900m south of the site. • Grade II listed Park and Garden (Sutton Courtenay Manor) lies 2.6km northwest of site • Nuneham Courtenay Grade I listed Park and Garden lies 3.7km north of the site. • Historic England advise that the site lies adjacent to its northern end to a Scheduled Monument (Settlement Site SE of Church). The potential impact on setting of that Monument, and the fact that it is possible that the archaeological interest extends beyond the scheduled area, need to be considered in determining what area, if any, of the site is suitable for mineral extraction. • Site does not lie in close proximity to any battlefields or World Heritage Sites.

© Adams Hendry Consulting Ltd. 474 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • The site is located in an area of archaeological interest. The northern side of the allocation abuts a Scheduled Monument (SM 243). This is the site of a settlement site. In the north part a number of cropmarks are visible. They also have distinct similarities to features within the scheduled area as such may require physical preservation. Transport and Access (Policy • Site has potential for direct access onto the A4130, which is part of the Oxfordshire Lorry C10) Route. • Access via the B4016 to the north of the site, maybe possible although this road is not part of the Lorry Route Network and a level crossing may prohibit access to the west. • No AM or PM peak traffic congestion identified within proximity to the site. • Site lies in close proximity to area with history of RTIs. • Conveyor link proposed to transport minerals to existing Sutton Courtenay Quarry for processing (west of the site). Public Rights of Way (Policy C11) • A public footpath follows the Eastern boundary of the site. • Restoration is proposed. Health and Amenity (Policy C5) • Residential dwellings in Didcot lie 75m to the south of the site and dwellings on the B4016 lie 75m north of the site. • Dwelling at Hill Farm lies 270m west of the site and another dwelling lies 175m west of the site. • Outline planning permission for 2,030 homes was granted in 2016 on a site adjacent to the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the Dalton Barracks buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 5 existing waste sites: Didcot Strategic STW, Sutton Courtenay, Hill Farm, Milton Park and (minerals and waste sites) Culham JET. • Site lies within 3km of 1 existing minerals site: Sutton Courtenay Quarry (Bridge Farm). • Site lies within 3km of 3 nominated waste sites: Sutton Courtenay Landfill (1,2&3), Culham Science Centre and Didcot STW. • Site lies within 3km of 2 nominated minerals sites: SG-17 Land at Culham and SG-67 Sutton Wick Quarry.

Conclusion

The site was nominated in 2009 and may therefore no longer be available. This site is promoted as an extension to Sutton Courtney Quarry and is within the Mineral Strategic Resource Area.

The site partially overlies BMV agricultural land and is adjacent to a Scheduled Ancient Monument. The site is also located close to existing minerals and waste operations and is adjacent to land with outline consent for a large housing development.

Notwithstanding the potential constraints of this site, there may be some potential for mineral working and the site will be subject to further assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

The nominated site lies to the east of the existing Sutton Courtenay quarry and waste management site, to the east of the Oxford to Didcot railway line. Current working is at Bridge Farm, to the north of the main Sutton Courtenay quarry and waste management site, north of the B4016. Extracted sand and gravel is transported by conveyor to the processing plant site within the main Sutton Courtenay quarry and waste management site. Access is via an internal access road from the A4130 at Didcot to the south.

Bridge Farm Mineral extraction was originally permitted at Bridge Farm on 04.08.2008 (MW.020/03); that permission has been subsequently varied. A small extension was permitted on 01.06.2018 (W.0127/16). There are 2 currently active planning permissions for mineral extraction at the Bridge Farm site:

MW.0094/18 permitted 06.05.2019 –S. 73 application for extraction of sand and gravel and restoration using in situ and imported clay materials to create a wet woodland habitat without complying with condition 1 (Date for completion of restoration) of planning permission no. P16/V0077/CM (MW.0001/16) such that it would be the same date for the completion of restoration as for planning permission no. P16/V2694/CM (MW.0127/16), at Bridge Farm Quarry.

Condition requires: The development shall cease and the site shall be restored no later than three years from the date of commencement of the development permitted by planning permission no. P16/V2694/CM (MW.0127/16) or no later than one year from the date of completion of extraction in phase 7 as permitted by planning permission no. P16/V2694/CM (MW.0127/16) or any subsequent planning permission which may be granted for that development subject to different conditions; whichever is the earlier.

MW.0127/16 permitted 01.06.2018 – small extension to Bridge Farm Quarry to extract sand and gravel and restoration to agriculture and lakes with reed fringes. Condition requires: The development shall cease, all associated pumps, plant and machinery shall be removed and the site shall be restored in accordance with the details set out in section 2 of the approved Planning Statement and the approved Further Information - Soils and land quality Version 1 dated 23/01/2017 and on approved drawings nos. S3/HAN/10/21 Rev F, S3/HAN/10/47 Rev A, S3/HAN/10/34 and S3/HAN/10/35 no later than three years from the date of commencement of the development.

Current (undetermined) planning application MW.0048/19 states that approximately 355,000 tonnes of sand and gravel remain to be extracted at Bridge Farm and that extraction is expected to be completed in 2021.

Processing Plant Site The processing plant site lies within the main Sutton Courtenay quarry, landfill and waste management site. It is covered by planning permission MW.0039/15 dated 03.08.2015 (the currently active planning permission), which also covers the current landfill area:

© Adams Hendry Consulting Ltd. 477 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 MW.0039/15 permitted 03.08.2015: to continue the development of permitted by P14/V0479/CM (for the deposit of non-hazardous waste including surcharging the existing landfill, extending the duration of landfill and clay extraction operations, temporary storage of PFA and ancillary activities to restoration) without complying with conditions 1, 10, 15, 17, 28, 30, 32 and 34, to amend the landfill phasing, restoration plan for phase 3, restored contours of phase 3 and the restoration method for phases 3 and 4 at Sutton Courtenay Landfill Site. Conditions on this permission require: Cessation of extraction of sand or gravel by 31.12.2020 or by two years from the final restoration of Bridge Farm Quarry; No extraction of clay after 31.12.2020 except clay required for landfill engineering works; No deposit of waste after 31.12.2030; All plant, buildings, machinery and structures to be removed and the land restored by 30.09.2036 (except plant or facilities for the monitoring or control of landfill gas or leachate and the access roads shown in brown and the land shown as “area of industrial development ‘coffin area’’' and ‘rail sidings/plant site’ on approved plan SC 2/2 – these have permanent permission); No more than 600,000 tonnes of waste shall be delivered to the site in any calendar year, of which not more than 350,000 tonnes shall be delivered by road.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records from within the site area indicate limited soil and clay overburden overlying 5.5m of sand and gravel with limited fine content. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Notable Habitats include waterbodies within 500m (several other waterbodies are on the other side of railway).

Records of European protected species include records for Great Crested Newt and several bat species in local area. Other protected and Notable species include records for Common Lizard, Grass Snake and Water Vole. Other nearby records exist for mammal, bird, amphibian, plant and invertebrates.

The closest LWS is Haywards Eyot LWS approximately 1.6km north-east. Thames Clifton to Shillingford CTA is approximately 3.3km east.

Biodiversity net gain should be achieved on the restoration of the site. There is further potential for improvement to surface water quality.

Overall the ecological impacts of the proposals are likely to be low/moderate. No significant impacts on any statutory or non-statutory site of nature conservation interest are anticipated. Given records for reptiles and water vole within and immediately adjacent to the site, a suite of ecological surveys must be undertaken.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site can be viewed from AONB from a distance but this is in the context of Didcot power station, industrial estate and other industrial uses. Any potential impacts are considered to be low.

New triangular shaped site is characterised by intensively farmed fields bounded by hedgerows and trees. Site boundaries defined by railway line (West), B4016 (North), Moor Ditch (East) and the A4130 / Didcot (South). Moor ditch and associated vegetation is important feature within the landscape.

In the wider context, there area is characterised by agricultural fields (north West), Didcot and waste processing provide context to the Northeast, East and South. The railway line forms effective boundary to between rural and industrial context. The site would not be perceived as an extension to Sutton Courtenay quarry in landscape and visual terms.

The site is in close proximity to Didcot and Appleford (up to ring road). The community reserve near Appleford Crossing is sensitive to development.

A PRoW runs along eastern boundary but is separated from site by Moor Ditch and mature vegetation. Views of the site are partly screened and views would be in the context of the landfill and power station. There may be occasional views from B4016 and local roads and selective views from edge of Didcot.

No known historic landscape constraints.

Overall the landscape and visual impact is considered to the moderate due to the encroachment of the site beyond the railway line into the rural countryside, the close proximity to Didcot and the visibility of the workings from adjacent PRoW, local roads and residential Didcot and Appleford.

Compliance with Policy C10: Transport - Highways Officer Assessment

The Local Highway Network has severe capacity and congestion issues in this local area. A routing agreement is currently in place to restrict HGV movements leaving the site via the B4016 – preference is for A4130.

The site is located adjacent to an area of land safeguarded to support the delivery of a new Thames River Crossing between Culham and Didcot, as set out in Core Policy 18 of the adopted Local Plan 2031 Part 1 and Policy TRANS3 of the emerging South Oxfordshire Local Plan 2034. The policies ensure that proposals for development that may be considered to impact the delivery of an identified transport scheme demonstrate that the proposal would not harm its delivery and planning permission will not be granted for development that would prejudice the construction or operation of the scheme.

This particular highway scheme is identified as of strategic importance to unlock growth in the Science Vale area. Furthermore, the Housing and Infrastructure Fund (HIF) bid was recently approved by Government, which has secured funding for four major projects in the district, including the strategic highway scheme for a new crossing over the River Thames. In the absence of HIF infrastructure, such as new river crossing and Clifton Hampden by-pass development, generating new peak hour movements are being resisted by OCC highways.

© Adams Hendry Consulting Ltd. 479 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 There are significant level differences towards the Didcot end of the site and OCC would not encourage a new access in this location without more information due to the likely river crossing road alignment scheme proposed nearby. OCC would not promote an access onto the B4016 without understanding more of the distribution of vehicles associated with the site - as site is close to village.

Conclusion

The site promoter is proposing that the minerals will be moved by conveyor to the existing Sutton processing plant (subject to crossing the railway) and to use the existing transportation arrangements as for the Sutton Courtney Quarry. Very limited vehicular access would be required from the A4130.

As operations at Bridge Farm to the north of the main Sutton Courtenay quarry are due to wind down in the next few years, some existing traffic would be removed from the highway network.

The site is located adjacent to an area of land safeguarded to support the delivery of a new Thames River Crossing between Culham and Didcot. As such any development at this site must not prejudice the construction or operation of the scheme which is identified as of strategic importance to unlock growth in the Science Vale area and which has recently been approved for Housing and Infrastructure Fund (HIF).

This may be a suitable site for allocation in the Sites Local Plan, as an extension to an existing site, free of Green Belt and AONB constraints and in southern Oxfordshire. Careful phasing to avoid cumulative impacts, particularly traffic with Sutton Courtney existing minerals and waste site.

SG-63: Finmere Quarry

Site Information (as nominated in 2018) Site Location Finmere Quarry Grid Reference SP626327 Administrative Area Cherwell Parish Finmere Site Nominee(s) AT Contracting & Plant Hire Limited Proposed Development Sharp sand and gravel extraction. Potential extension to Finmere Quarry.

Site Area 10ha Estimated annual 100,000 tpa output Estimated Reserves Estimated total yield of 0.3 mts (including depth/ Estimated working depth of 2.5m Estimated overburden of 1.2m overburden) Proposed Restoration To agriculture Access Existing access onto A421. Estimated Traffic 21 HGV movements per day Movements (Note: OCC Transport – Have queried the number of HGV movements in the application due to the period of operation (5 months per year) and the concrete batching plant). Year of 2023 Commencement Lifetime of 5 years Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within Mineral Strategic Resource area or the Mineral Safeguarding Area. Strategy – Strategic Resource • Site is located in the northern part of the county (Cherwell). Areas (Policy M3) • Site is proposed as an extension to Finmere Quarry. • Estimated total yield of 300,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan but does lie adjacent to HS2 Safeguarding Zone. Biodiversity and Geodiversity • Site lies in excess of 5km from International/European designated sites. (Policy C7) • Tingewick Meadows SSSI lies 2.5km to the southeast of the site. • Stonepit Spinney lies 1km to the north of the site and Diggings Wood lies 750m to the southwest (Ancient Woodland). • Site does not lie close to any LNRs, or NNRs. Landscape / Visual (Policy C8) • Site lies over 5km from an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a principal and secondary aquifer. • Site does not lie within Flood Zones 2 and 3. Air Quality (Policy C5) • Site is not located within 1km of AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 3 agricultural land. • Restoration proposed. Historic Environment (Policy C9) • Site lies within 300m of a Grade II listed farmhouse to the southwest. • Listed buildings in Finmere lie 650m to the east of the site. • Scheduled Monument (Beaumont Castle) lies 1.6km to the northwest of the site. • A Grade I listed Park and Garden (Stowe) lies 4.1km to the northeast of the site. • Site lies within 1.5km of Mixbury Conservation Area to the north west of the site. • Site does not lie close to any battlefields or World Heritage Sites. • The site is located in an area of archaeological interest. There is a cropmark within the allocation which appears to be a circular enclosure, possibly a barrow. In advance of the extraction to the south a Bronze Age cremation cemetery was recorded. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies adjacent to the A421 on the Oxfordshire Lorry Route. C10) • Site lies in close proximity to an area with history of RTIs. • No AM or PM peak traffic congestion areas identified within proximity to site. Public Rights of Way (Policy C11) • Public bridleway crosses the centre of the eastern site. Another PRoW runs in a north south direction approximately 250m to the east of the site. Health and Amenity (Policy C5) • Nearest residential dwellings 200m and 250m to the east of the site.

© Adams Hendry Consulting Ltd. 483 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Warren Farm 290m north of the site. • Farmhouse 300m southwest of the site. • Dwellings in Finmere approximately 500m east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 1 existing waste site: Finmere Quarry. (minerals and waste sites) • Site lies within 3km of 1 existing minerals site: Finmere Quarry. • Site lies within 3km of 1 nominated waste site: 011 Finmere Quarry. • There are no nominated minerals sites within 3km of the site.

Conclusion

Site does not lie within either the Mineral Strategic Resource Area of the Mineral Safeguarding Area. However, the nominated site is proposed as an extension to the existing Finmere quarry.

The nominated site would potentially use the existing access direct onto the Oxfordshire Lorry route Network (A421).

The site is considered to have potential to for mineral development due to its co-location with an existing extraction site and will be subject to further detailed assessment

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

There is no relevant minerals or waste planning history on the nomination site itself.

There are four currently active planning permissions and one expired permission at the adjoining Finmere Quarry and Landfill Site:

MRF (Site lies within non-hazardous landfill permission area.) MW.0139/15, permitted 29.01.2016: Section 73 application for planning permission to continue development without complying with Conditions 1, 7, 17 and 26 (to allow the storage of Refuse Derived Fuel (RDF) and Solid Recovered Fuel (SRF) outside the storage bay at the consented MRF (the subject of planning permission 10/00361/CM), to amend the operational hours of the MRF and to extend the acoustic barriers) of planning permission reference 15/00245/OCC. Conditions require: • Acceptance of waste shall cease by 31.12.2020; and all buildings, plant and machinery shall be removed, and restoration be completed by 31.12.2021; • Annual throughput of waste shall not exceed 150,000 tpa.

Sand & Gravel Extraction and Inert Landfill (South eastern mineral extraction area – adjoins area nominated for secondary aggregate recycling to the east)

© Adams Hendry Consulting Ltd. 485 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 MW.0083/17, permitted 26.01.2018: Section 73 application to continue sand and gravel and clay extraction for use in on-site landfill engineering permitted by planning permission no. 10/01515/CM without complying with conditions B1, B2, B3, B8, B9, B14, B16, B17, B20, B26, B32, B35, B37 and B39 to enable the development (including restoration) to continue until 30th September 2031, alternative screening to be provided along the eastern boundary and the updating or deletion of conditions which no longer apply. Conditions require: • Cessation of mineral extraction by 06.01.2030; • Cessation of deposit of quarry reject material by 06.01.2031; • Completion of restoration 30.09.2031. • Excavated minerals shall not be transported onto the public highway and shall only be used in the area the subject of planning permission MW.0004/17 (superseded by MW.0139/15 – the non-hazardous landfill area).

South West mineral extraction area (south west of disused railway line) MW.0142/10 permitted 21.12.2010: To continue development without complying with condition A3 of planning permission reference APP/U3100/A/06/2030592 (extension to Finmere Quarry to extract sand and gravel from land south-west of Finmere, including the relocation of plant and restoration of the quarry using imported inert waste to agriculture, woodland and grassland at Finmere Quarry landfill, Banbury Road, Finmere, MK18 4AJ) for an extension of the life of the development of the consented extension to Finmere Quarry This permission was implemented but has expired because a condition required mineral extraction to cease by 31.12.2016. (See below, application MW.0142/16 to continue this development.)

Current applications There are seven current applications for the Finmere Quarry site that are yet to be determined:

• MW.0142/16 – Continuation of development without complying with conditions A1, A3, A22 and A33 of planning permission reference 10/01516/CM (MW.0142/10) to provide for an extension of the life of the development of the consented extension. The application states that remaining sand and gravel deposits total 305,000 cu. m. (= approx. 460,000 tonnes) which will take 5 years to extract; and that restoration with 351,000 cu. m. of inert fill material will take a further 2 years. This relates to expired permission MW.0142/10 granted 21.12.2010 (see above) for sand and gravel extraction from land to south west of Finmere Quarry and Landfill site, but with the processing plant located on the area now nominated for secondary aggregate recycling and using the existing quarry/landfill access.

• MW.0027/19 – Extension to the area for non-hazardous waste landfill. (This is for approximately the same area as the area nominated for landfill (non-hazardous waste) extension.)

• MW.0030/19 – Extension to area approved for sand and gravel extraction and retention of processing and concrete batching plants.

© Adams Hendry Consulting Ltd. 486 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 (This is for extraction of sand and gravel from land to the north of the existing quarry & landfill site, the same area as mineral site nomination SG- 63 but including retention of the processing etc plant in the area nominated for secondary aggregate recycling.)

• MW.0031/19 – Application for secondary aggregate recycling. (This is for the area nominated for secondary aggregate recycling.)

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource Limited borehole records available to assess quality. Trail pit record extracted approximately 1km to the east / south-east of the site shows silty sandy clay and chalky gravel at a depth of around 1.9m.

Poor.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment There are no irreplaceable habitats within or adjacent to the site. Notable Habitats include Finmere Plantation woodland within the wider permitted site, bound by existing operations and ponds.

Records exist for European protected species including Great Crested Newt (existing licence for translocation) and for several bat species. Other protected/notable species include Badger, Smooth Newt, Grass Snake and numerous other notable species

The land is not part of the existing permitted area but is adjacent to it. Ecological surveys undertaken to data have confirmed the site provides opportunities for a number of protected species. Mitigation measures are expected to limit impacts on protected species, with no anticipated residual harm. Restoration proposals will likely improve biodiversity within the site.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting.

The site comprises two agricultural fields to the north of Finmere Quarry and landfill complex.

Immediate landscape context of A421 to the north, disused railway line to the west and landfill and recycling operations to the south, reduce landscape character sensitivity.

Restoration offers opportunities for landscape enhancements in the long term.

© Adams Hendry Consulting Ltd. 487 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 The site is generally quite well screened but occasional glimpsed views from A421 are possible especially during winter months.

The landscape impact of this allocation is considered to be slight due to the existing landscape context of former quarry, landfill, MRF and major road. Visual impacts are considered to be moderate due to development being viewed in context of other waste uses on site.

Overall the landscape and visual impact is considered to be minor.

Compliance with Policy C10: Transport - Highways Officer Assessment

Allocation of the site would have no impact on the Oxfordshire lorry route network with good existing access direct on to A421 (Freight Priority Network - Primary), without passing through any villages.

The existing access has good visibility with gates set well back. There is a right turn filter lane from the A421.

Conclusion

The site lies within northern Oxfordshire outside a strategic resource area. Core Strategy Policy M3 makes it clear that the principal locations for aggregate minerals extraction will be within the strategic resource area and that sites will be allocated for sharp sand and gravel working to meet the requirement in Policy M3 such that approximately 25% of the additional tonnage requirement is in northern Oxfordshire and approximately 75% is in southern Oxfordshire.

The site has good access to the lorry route network, would not have a significant landscape or visual impact and subject to appropriate mitigation, would not have an adverse impact on ecological receptors. However, whilst the area has a long history of mineral working, given that the site does not accord with the general principles set out in Policy M3, it is not recommended that the site is allocated in the Sites Allocation Document unless it can be demonstrated the requirements set out in Policy M2 cannot be met on alternative sites within the strategic resource area.

SG-67: Sutton Wick Quarry

Site Information (as nominated in 2018) Site Location Sutton Wick Grid Reference SU 493947 / SU 496942 Administrative Area Vale of White Horse / South Oxfordshire Parish Sutton Courtenay and Culham Site Nominee(s) H Tuckwell & Sons Ltd

Proposed Development Sharp sand and gravel extraction. Potential extension to Sutton Wick Quarry. Site Area 3.5 hectares / 6.5 hectares Estimated annual Unknown output Estimated Reserves Estimated reserves of 0.2 mts (I&O (including depth/ 2018) Estimated working depth of between overburden) 2-4m Estimated overburden of 0.3-1m Proposed Restoration Lakes and wetland restored on finishing extraction from each parcel. Some land will be returned to dry agricultural land as well. Access Existing access via Stonehills Lane. Estimated Unknown Traffic Movements Year of On completing the existing Camas Commencement Land in 2 years’ time but before commencing extracting from the plant site. Lifetime of 2 years remaining in the Camas Operation land.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site does not lie within Mineral Strategic Resource Area or the Minerals Safeguarding Area. Strategy – Strategic Resource • Site is located in the southern part of the country (Vale of White Horse / South Oxfordshire). Areas (Policy M3) • Site proposed as a possible extension to the Sutton Wick Quarry. • Estimated total yield of 0.2 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Cothill Fern SAC lies approximately 5.5km to the north west of the northern site. (Policy C7) • Little Wittenham SAC lies approximately 6.8km to the east of the southern site. • The northern site lies approximately 2km from Ancient Woodland to the northeast. • The northern site is approximately 2km from two Priority Habitat Creation and Restoration schemes to the north of the site. • The northern site lies approximately 2.1km of Culham Brake SSSI to the north east. • Neither site lies close to any LNRs, or NNRs. • Abbey Fishponds Local Nature Reserve lies 3.5km to the northeast of the site. • The southern site is approximately 1.5km from a Proposed Local Wildlife Site to the south (Kelart’s Field). Landscape / Visual (Policy C8) • Site lies over 3km from an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4)) • Site overlies a secondary aquifer. • Site lies within Flood Zones 2 and 3. Air Quality (Policy C5) • Site not located within 1km of AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 4 agricultural land. Historic Environment (Policy C9) • The southern site is close to a large number of listed buildings and the conservation area in Sutton Courtney to the east of the site. The closest listed building is approximately 115m from the south of the site. • The southern site lies approximately 600m from a Scheduled Monument (Settlement Site) to the west. Sutton Wick Settlement Site lies 1.2km northwest of the northern site. • Grade II listed Park and Garden (Sutton Courtenay Manor) lies 200m east of the site. • Albert Park (Grade II listed) lies 2.3km north of the northern site. • Site does not lie in close proximity to any battlefields or World Heritage Sites. • Site is within a landscape dominated by old mineral workings as such there are currently no known historic landscape constraints. • The site is located in an area of archaeological interest.

© Adams Hendry Consulting Ltd. 491 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Transport and Access (Policy • Site access would be potentially via Stonehills Lane (2km) to the B4017, a local access route C10) on the Oxfordshire Lorry Route. • From the entrance to Stonehills Lane, the site is approximately 2.5km from the A34 to the north (through Caldecott, Abingdon) via the B4017. • Site lies in close proximity to an area with history of RTIs (2 serious RTIs within 3km of the site). • AM and PM peak traffic congestion areas identified within close proximity to the site. • Existing access is via Stonehills Lane. Public Rights of Way (Policy C11) • Public bridleway lies adjacent to western edge of the northern site. • Restoration proposed. Health and Amenity (Policy C5) • Nearest residential dwelling is approximately 60m south west of the site. • Another dwelling lies 80m east of the site. • Dwellings in Sutton Courtenay are 100m south east of the site. • The northern site is approximately 675m from residential dwellings to the west on Stonehill Lane. Green Belt (Policy C12) • The southern site lies within the Green Belt. • The northern site lies adjacent to Green Belt. • Restoration proposed. Aerodrome Safeguarding (Policy • Site lies within Dalton Barracks buffer of airport safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 7 existing waste sites: Glebe Farm, Wantage Strategic STW, Tubney Wood, Drayton WRRC, (minerals and waste sites) Stanford-in-Vale HWRC, Didcot Power Station and Swannybrook Farm. • Site lies within 3km of 2 existing minerals sites: Sutton Courtenay Quarry (Bridge Farm) and Sutton Wick Quarry. • Site lies within 3km of 2 nominated waste sites: 010 Sutton Courtenay Landfill (1,3&3) and 276 Oday Hill. • Site lies within 3km of 1 nominated minerals site: SG-62 Appleford.

Conclusion

The nominated site is fragmented into two parts, with one lying adjacent to the south east of the existing processing plant associated with Sutton Wick Quarry, and the other lying approximately 800m to the south east of the existing processing plant.

Both parts of this site nomination can be accessed via Stonehill Lane, a single-track route subject to a 15-mph speed restriction, although the northern part of the site nomination appears to benefit from direct access onto this connecting route. A number of residential properties lie adjacent to this route and the potential impact on residential amenity should be further considered. This route connects onto the Oxfordshire Lorry Route Network (B4017), approximately 2.0km to the west of the site.

© Adams Hendry Consulting Ltd. 492 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 The southern most of the two site areas lies within the Green Belt and may have less potential than the northern site.

The nominated site(s) does not lie within the Mineral Strategic Resource Area, nor the Mineral Safeguarding Area but would be a potential extension to Sutton Wick Quarry. Based on the outcome of this initial assessment, the site(s) is considered to have some potential as a future mineral development and will be subject to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

PLANNING HISTORY

There is no relevant minerals or waste planning history on the nomination sites themselves. These sites are adjacent to the existing Sutton Wick (Oday Hill) Quarry. The quarry has a long and complex planning history but there are two main currently active planning permissions, for the plant site and the Camas land which is the current remaining mineral extraction area.

Sand and gravel processing plant site MW.0099/18 permitted 19.12.2018: Section 73 application to continue the development permitted by permission no P13/V2763/CM (MW.0124/13) (to retain and operate the processing plant and ancillary operations). This permission allows retention of the processing plant and extraction of the underlying sand and gravel. Conditions require: • processing plant is to be removed by 31.12.2025; • extraction of sand and gravel to cease by 31.12.2027; • site to be restored by 31.12.2028.

Camas Land MW.0098/18 permitted 18.12.2018: Section 73 application to continue the development permitted by permission no P16/V3191/CM (MW.0139/16) (for the progressive extraction of sand and gravel, importation of inert waste material with restoration to nature conservation and an agricultural reservoir). Conditions require: • Extraction of sand and gravel to cease by 01.03.2022; • Site to be restored by 01.03.2025.

The site nomination (March 2018) states there are 2 years extraction remaining in the Camas land.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Nomination form suggests overburden of between 0.3m and 1m with depth of working between 2m and 4m.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within or adjacent to the site. Notable habitats include floodplain grazing marsh on site. It is also in close proximity to River Thames and other waterbodies and to deciduous woodland.

There are numerous records for bats (European protected species) within the area. Other protected/notable species include records for of mammal, bird, amphibian, plant and invertebrates. Otter, Water Vole and various wildfowl recorded on site.

Kelart’s Field proposed Local Wildlife Site lies approximately 1.5km to south. Thames Radley to Abingdon Conservation Target Area (CTA) lies approximately 1.3km north-east.

Overall there are several potential ecological impacts which will need to be fully assessed and mitigated, including the loss of floodplain grazing marsh and impacts on the river and associated species.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting.

Both parts of the site nomination are next to previous quarry pits.

The northern site comprises an agricultural field with gappy or missing hedgerow boundaries. The landscape context predominately comprises existing quarry, sewage treatment plant and other industrial operations, as well as former gravel pits and agricultural uses.

The southern site is arable field bounded by hedgerows, located between former gravel pit and Drayton Rd. This site comes close to Sutton Courtney conservation area and is considered more sensitive in landscape terms compared to the northern site.

A PRoW and cycle route runs along the western boundary of the northern site with views into the site. More distant views from other PRoWs might also exist.

Occasional views from Drayton Road (B4016) into the site are likely. Selected views from conservation area might also exist.

Site operation expected in the short term reducing visual impacts.

Overall the northern part is considered to have a slight landscape and visual impact due to the context of quarrying and other industrial uses. Restoration of site has potential to deliver landscape and ecological benefits.

Compliance with Policy C10: Transport - Highways Officer Assessment

Existing access onto the B4017 looks to be adequate.

Access out onto B4017 and then would have to route through Abingdon to the Marcham Interchange or across the Thames or south through Drayton to the Milton Interchange, but through the Steventon lights. Both of these routes expereince peak hour congestion.

Conclusion

The site has reasonable access to the lorry route network but would rely on routes experiencing peak hour congestion. The southern part of the nominated site is within the Green Belt, where mineral extraction is not inappropriate provided it preserves openness and does not conflict with the purpose of including land within it.

Given that the site does not accord with the general principles set out in Policy M3, it is not recommended that the site is allocated in the Sites Allocation Document unless it can be demonstrated the requirements set out in Policy M2 cannot be met on alternative sites within the strategic resource area.

Site SS-03 & CR-17: Hatford Quarry South Extension

Site Information (as nominated in 2009) Site Location Hatford Quarry South Extension

Grid Reference SU 331 949

Administrative Area Vale of White Horse

Parish Stanford in the Vale

Site Nominee(s) Hatford Quarry Ltd

Proposed Development Soft sand and Crushed rock extraction. Extension to Hatford Quarry. Site Area 27.4 ha

Estimated annual 100,000 tpa output Estimated Reserves Estimated yield of 1.7mt soft sand (including depth/ Estimated yield of 1.8 mt crushed rock overburden) Estimated working depth of 20m Estimated overburden of 1.2m Proposed Restoration Low level restoration to agriculture in accordance with phasing schedule. Access Access from B4508 Fernham Road Estimated 70-80 movements for combined Traffic sand/limestone working. Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Oxford Strategy – Strategic Resource to Faringdon) and for crushed rock (East / South East of Faringdon), in the southern part of the Areas (Policy M3) county (Vale of White Horse). • Greenfield site adjacent to the Hatford Quarry, proposed as a potential extension. • Site lies within 1km of the A417 Oxfordshire Lorry Route. • Estimated site yield is 1.7mt soft sand and 1.8 mts crushed rock. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies approximately 200m from Shellingford Crossroads Quarry SSSI. (Policy C7) • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. • Site located in excess of 5km from International / European designated sites. The nearest SAC is Hackpen Hill, approximately 9km south of the site. • Hatford Sand Pit adjacent to the site is a Local Geological Site Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site not within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site adjacent to a flood zone 2 and flood zone 3 area. • Proposed site use would be water compatible. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site is within an area of predominantly Grade 2 agricultural land with the south west corner of the site overlying Grade 3 agricultural land. • Restoration proposed to return land to agricultural use. Historic Environment (Policy C9) • Site lies adjacent to the Hatford Conservation Area. • There are 6 listed buildings within 100m east of the site in Hatford. • Site lies within 2km of a Scheduled Monument to the north. • There are currently no known archaeological or historic landscape constraints. Transport and Access (Policy • Site lies within 1km of the A417 Oxfordshire Lorry Route. C10) • Site connects to the A417 Oxfordshire Lorry Route via the B4508 (Fernham Road). The B4508 passes two residential dwellings, one of which is located on the junction with the A417.

© Adams Hendry Consulting Ltd. 499 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies 1km from a fatal RTI on the A417 and within 3km of three serious RTIs (2 on the A417 and 1 on the B4508). Public Rights of Way (Policy C11) • Public footpath runs adjacent to eastern side of the site. Health and Amenity (Policy C5) • Residential dwellings in Hatford are approximately 200m from the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton buffer of airport safeguarding. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 3 existing minerals sites: Shellingford Quarry, Chinham Farm Quarry and Hatford Quarry. • Site lies within 3km of 3 nominated waste sites: 283 Hatford Quarry Ext, 229 Shellingford Quarry and 230 Chinham Farm. • Site lies within 3km of 7 nominated minerals sites: SS-07/CR-24, SS-08/CR-16, SS-12/CR-12, SS-15/CR-11, SS- 16/CR-21, SS-18/CR-22 and SS-19/CR-23.

Conclusion

The site lies within the mineral strategic resource area (MRSA) in the southern Oxfordshire area and is a potential greenfield extension to the existing Hatford Quarry. The site is predominantly located on Grade 2 agricultural land. There are also a number of residential dwellings approximately 200m of the site at Hatford, the potential impact on which will need to be considered further.

Given the site’s location within the MSRA and the connectivity with the Oxfordshire Lorry Route, this site will be carried forward to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Existing Hatford Quarry is to north of site. Quarry access road runs through this site to B4508. The currently operational planning permission for mineral extraction at Hatford quarry is:

MW.0153/12, permitted 16.09.2013: Extension of quarry for the extraction of limestone and sand with restoration to agriculture; associated processing operations and plant, retention of site office and weighbridge. (Western extension to existing quarry.) Condition requires extraction of minerals to cease within seven years of commencement; and buildings, plant and machinery to be removed and restoration completed by 16.09.2021.

No publicly available information on remaining permitted reserves; assume will be worked out by current permission end date.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource SS-03: Limited borehole records available to assess quality. Records along the southern boundary show around 9m of brown, white and grey sands below the limestone beds. Good.

CR-17: Limited borehole records available to assess quality. Records along the southern boundary of the site indicate potentially good quality of limestone with limited overburden. Good.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

No irreplaceable habitats are recorded to be within or adjacent to the site and only Frogmore Brook, along the eastern boundary, is regarded as a notable habitat.

A number of European protected species exist within the local area including the Great Crested Newt and several species of bat. Other protected and notable species include several mammals, birds, amphibians, plants and invertebrates.

The site is partially within Oxon Heights Conservation Target Area (CTA). Chaslins Copse Local Wildlife Site lies approximately 1.3km to the west.

© Adams Hendry Consulting Ltd. 501 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Overall the ecological impacts of the proposals are likely to be low. No significant impacts on any statutory or non-statutory site of nature conservation interest are anticipated.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. It comprises arable fields West of Hatford where hedgerow boundaries are low or absent giving a sense of openness. Frogmore Brook along the eastern boundary acts as a boundary and triggers a change in character. Area east of brook towards Hatford are more sensitive in landscape terms.

Although only a short distance from the existing Hatford Quarry this site nomination might be perceived as a new quarry rather than an extension in LVIA term due to separation by Frogmore Brook.

The site is visible from the PRoW, Fernham Rd and Hatfield settlement / conservation area, the boundary of which is approximately 80m away. Mitigation in the form of native planting and bunding will assist in mitigating visual impacts from the road but is unlikely to be fully successful in mitigating views from Hatford. Restoration has potential to deliver landscape enhancements in the long term.

The site itself is not considered sensitive in landscape terms but sensitive local context (eg Hatford conservation area).

Overall this site nomination is expected to substantially affect the landscape character and views due to the intrusive nature of the development, its large size and its close proximity to Hatford conservation area impacting on the setting and views.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts would need to be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

The A417 is a strategic route and is known to have capacity issues in the peaks.

The existing access to the site appears acceptable.

Conclusion

The site lies within Mineral Strategic Resource Areas for soft sand and crushed rock and is within 1km of the A417 on the Oxfordshire Lorry Route.

The site is nominated as an extension to Hatfield Quarry which has permission for the extraction of limestone and sand until 2020/21 with restoration to be completed by September 2021.

The ecological impacts of extraction are anticipated to be low, however the effect on landscape character is expected to be significant due to its size and close proximity to Hatford conservation area.

© Adams Hendry Consulting Ltd. 502 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 There are a number of existing and nominated mineral and waste sites within 3km of the site and therefore cumulative impacts will need to be considered taking into account the overall requirement for crushed rock and soft sand over the plan period set out in the Core Strategy.

SS-04: Land at Pinewoods Road

Site Information (as nominated in 2018) Site Location Land at Pinewoods Road, Longworth

Grid Reference SU 384984

Administrative Area Vale of White Horse

Parish Longworth

Site Nominee(s) Hanson Aggregates Proposed Development Soft sand extraction. Potential New Quarry. Site Area 29ha Estimated annual Unknown output Estimated Reserves Estimated total yield of 1.1 mts (including depth/ Estimated working depth of 5-8m Estimated overburden of 0.8m overburden) Proposed Restoration Agriculture with biodiversity improvements achieved through progressive restoration. Access Access off Pine Woods Road (150m from A420). Estimated Site likely to generate 25 lorry Traffic movements outbound & inbound. Movements Year of Not before 2023 Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area (Corallian Ridge – Oxford to Faringdon) in Strategy – Strategic Resource the southern part of the county (Vale of White Horse). Areas (Policy M3) • Site is proposed as a potential new quarry. • Estimated site yield is 1.1 mts. District Local Plan Allocation • Site is not allocated in a District Local Plan. • Site included within the adopted Longworth Neighbourhood Plan (2016). This requires development proposals to have special regard to the setting, amenity and character of nearby dwellings, contribute to local distinctiveness, and protect and enhance nature conservation, watercourses, ecology and landscape character. Biodiversity and Geodiversity • Site lies approximately 400m to the north east from Lamb and Flag Quarry SSSI. (Policy C7) • The site lies adjacent to String Copse ancient woodland and there is a further area of ancient woodland approximately 60m of AW to the west. • Natural England note that there is BAP to the west of the site on the other side of Pine Woods Road. • Site lies in excess of 5km from International/European designated sites. Nearest SAC is Cothill Fen, approximately 7km east of the site. • Site does not lie within 1km of a LNR or NNR. Landscape / Visual (Policy C8) • Site does not lie within 3km of an AONB. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in proximity to an AQMA Soil Resources (Policy C6) • Site lies within an area of Grade 2 agricultural land. Historic Environment (Policy C9) • A cluster of listed buildings relating to Longworth Manor, including the Grade II listed Manor Farmhouse lie approximately 600m to the north • The Grade II Registered Historic Park and Garden of Hinton Manor lies approximately 600m to the north-west. • There is a Grade II* building (Tithe Barn) approximately 150m to the east. • Site lies within 130m of a Scheduled Monument (Barn at Longworth House) to the east. • Site lies within 250m of Longworth Conservation Area. • There are currently no known archaeological constraints to this allocation. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies adjacent to the Oxfordshire Lorry Route Network (A420). C10) • Site lies in proximity to areas with identified AM and PM peak traffic congestion.

© Adams Hendry Consulting Ltd. 506 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies in proximity to area with history of ‘serious’ RTIs. Public Rights of Way (Policy C11) • A public right of way crosses the site. Health and Amenity (Policy C5) • Site lies approximately 50-60m from residential dwellings on Pine Woods Road to the east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within Dalton Barracks and the northern part of the site also lies within RAF Brize M10) Norton airport safeguarding one.

Potential Cumulative Impact • Site lies within 3km of 1 existing waste site: Swannybrook Farm. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • There are no nominated minerals sites within 3km of the site.

Conclusion

The site is a greenfield site and appears to be in use for agricultural purposes on best and most versatile agricultural land. It is within the MSRA and adjacent to the Oxfordshire Lorry Route Network (A420).

There are a number of heritage assets within close proximity of the site, the settings of which would need to be taken into account in determining whether the site should be allocated. Consideration should also be provided to the residential dwellings which lie to the east of the site. Sufficient stand-off distance is likely to be required which may impact viability due to a reduction in the workable area. A public footpath also crosses the site and would require temporary diversion to avoid workings.

Based on its location within the MSRA and its proximity to the Oxfordshire Lorry Route Network, the site is considered to have some potential as a mineral working site for sharp sand and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

Previous application for same site and quantity of mineral as site nomination was refused permission in 2012: MW.0080/11, refused 03.05.2012: Extraction of sand, construction of new access to Pinewoods Road, construction of internal access road to stockyard, laying out of conveyor to extraction area, stripping and temporary storage of soils and restoration of land west of Pinewoods Road, Longworth.

Reasons for refusal: Contrary to Minerals and Waste Local Plan policy PE3 and no urgent need for soft sand reserves. (NB policy PE3 of the MWLP 1996 has been replaced by the M&W Core Strategy 2017.) Inconsistent with emerging M&W Core Strategy which has a policy preference for extensions over new sites. Adverse impact on landscape, contrary to Vale of White Horse Local Plan policy NE7. (This is a saved policy of the VoWHLP 2011 and is currently still valid.)

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Limited borehole records available to assess quality. A borehole record is found approximately 100m to the east of the site and shows considerable amount of shale and stone overlying a much thinner layer of sand.

Poor - Fair

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Irreplaceable habitats adjacent to the site include String Copse ancient woodland and Ashen Copse approximately 50m to east. There are other areas of ancient woodland within 1km of the site.

Notable habitats include adjacent woodland and waterbodies within the local area.

Records exist for European protected species including Great Crested Newt and several bat species in local area. Records exist for several protected and notable mammal, bird, amphibian, plant and invertebrate species. Wild Pansy has been recorded on-site.

© Adams Hendry Consulting Ltd. 508 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 No significant impacts on any statutory or non-statutory site of nature conservation interest are anticipated.

Newhouse Covert Local Wildlife Site (LWS) lies approximately 1.2km to the south and several other LWSs within 2km. The site is approximately 800m from West Oxon Heights Streams, Hills, Woods & Parks Conservation Target Area (CTA).

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting.

It is a new large site that is characterised by large intensive arable fields on gently sloping ground. Mature hedgerows and trees define external boundaries, internal hedgerows have been largely lost.

The area is of moderate landscape sensitivity despite proximity to the A420. Restoration offers opportunities for landscape enhancements in the long term.

Occasional views of the site from Pine Woods Road are possible and there would be an impact on views from a small number of residential properties.

Overall the landscape and visual impact of this site allocation is considered to be moderate due to the large size and isolated nature of the site, the rural landscape character context and the medium impact on public views.

Compliance with Policy C10: Transport - Highways Officer Assessment

No transport issues have been identified.

Conclusion

The allocation of this site would be contrary to Policy M4 of the adopted Oxfordshire Minerals and Waste Core Strategy which prioritises the extension of existing quarries (where environmentally acceptable) before working new sites. The site is in relatively close proximity to a number of heritage assets and residential properties, consists of best and most versatile agricultural land and is of moderate landscape sensitivity.

Unless there is an urgent need for soft sand reserves which cannot be met on an alternative site in a more environmentally acceptable way this site should not be allocated in the Minerals and Waste Site Allocations Local Plan.

Site SS-05: Land at Kingston Bagpuize

Site Information (as nominated in 2009) Site Location Land at Kingston Bagpuize

Grid Reference SU 425 973

Administrative Area Vale of White Horse

Parish Frilford

Site Nominee(s) Hills Quarry Products Ltd

Proposed Development Soft sand extraction. Potential new quarry.

Site Area 30 ha

Estimated annual 60,000 tpa output Estimated Reserves Estimated yield of 0.5 mts (including depth/ Estimated working depth of 5m Estimated overburden of 0.9m overburden) Proposed Restoration To be determined Access Existing access onto A415

Estimated Average vehicle movement Traffic removing sand – 12 per day Movements Year of Unknown Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Area (Corallian Ridge – Oxford to Faringdon) in the Strategy – Strategic Resource southern part of the county (Vale of White Horse). Areas (Policy M3) • Site is proposed as a potential new quarry. • Estimated total yield is 500,000 tonnes. District Local Plan Allocation • Site is not allocated in a District Local Plan. • A gas pipeline runs along the northern edge of the site, to the south of the A415. • The site falls within an area of archaeological constraint; potential Roman Villa site. Biodiversity and Geodiversity • Site lies within approximately 850m of Frilford Heath, Ponds and Fens SSSI. (Policy C7) • Site does not lie within 1km of Ancient Woodland. • Site does not lie within 3km from a SAC. • Cothill Fen SAC (International / European designated site) is approximately 3.5km to the north east of the site. • Site does not lie within 1km of an LNR or NNR or Oxfordshire Local Wildlife Site. Landscape / Visual (Policy C8) • Site does not lie within 3km of an AONB. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • There are no AQMAs within the vicinity of the site. Soil Resources (Policy C6) • The majority of the site (approximately 85%) is Grade 2 agricultural land with the remainder Grade 3 Historic Environment (Policy C9) • There are a number of listed buildings within 2km of the site, the closest being the Church of St Luke a Grade II listed building approximately 700m to the south of the site • Site lies approximately 1.3km from a Scheduled Monument to the south east (Site SE of Noah’s Ark Inn, Frilford) and 3.3km from a Scheduled Monument to the east (Settlement site N of Cow Lane). • The site is located within an area of considerable archaeological interest. There are records of a Roman Villa being identified and excavated within the allocation by Sir Arthur Evans. Several rooms were found along with a bathhouse or cistern. No formal excavation report was published, and it is difficult to establish where this was found. Several watching briefs have been undertaken in the area and no evidence of Romano British settlement or activity has been identified. A geophysical survey has identified some possible enclosures and settlements but no suggestion of a villa. • There are currently no known historic landscape constraints Transport and Access (Policy • Site is located off the A415 which is on the Oxfordshire Lorry Route Network (A415). C10) • There are areas of AM and PM peak traffic congestion identified within proximity to the site.

© Adams Hendry Consulting Ltd. 512 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • The site lies in proximity to areas with a history of ‘serious’ RTIs. Public Rights of Way (Policy C11) • A public footpath runs east-west along the southern boundary of the site. There is another public foot running north-south opposite the site. Health and Amenity (Policy C5) • There is a residential dwelling approximately 40m to the west of the site and also approximately 100m to the east of the site. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • The site lies within the Dalton Barracks airport safeguarding zone. M10)

Potential Cumulative Impact • Site lies within 3km of 1 existing waste site: Swannybrook Farm. (minerals and waste sites) • There are no existing minerals sites within 3km of the site. • There are no nominated waste sites within 3km of the site. • Site lies within 3km of 1 nominated minerals site: SS-17.

Conclusion

The site was nominated in 2009, there is therefore uncertainty as to whether the site is still available.

The site does not operate as an existing minerals site. A small part of the site appears to be in use as a recycling facility with the rest in agricultural use. The majority of the site is best and most versatile agricultural land.

There is potential for access from the site directly onto the A415 (Kingston Road). Consideration would need to be given to the residential dwellings which lie adjacent to the west of the site and within 100m to the east of the site. Sufficient stand-off distance is likely to be required.

For these reasons, the site is considered to have some potential as a mineral working site for sharp sand and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Limited borehole records available to assess quality. Those which lie near to the site indicate good brown and grey sand resource with evidence of overlying limestone deposits. Fair – Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within or adjacent to the site. Notable habitats include waterbodies and woodland within close proximity. The site is approximately 550m from River Ock.

Records exist for Great Crested Newt and several bat species in local area (European protected species). Other protected/notable species include several protected and notable mammal, bird, amphibian, plant and invertebrate species.

Overall the habitats within the site are not likely to pose a significant constraint.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting.

It is a new stand-alone site characterised by a chicken farm and a large open arable field.

Landscape context of open intensive arable fields with isolated developments such as Millets farm centre, waste management operations and other farming- related uses.

There would be occasional views from the A415 and views from a few residential properties might be affected.

Overall the landscape and visual impact of the allocation is considered to be moderate due to the isolated nature of the site in a predominantly rural open landscape that is also moderately sensitive in views and in historic character terms.

Landscape restoration has the potential to deliver benefits in landscape character terms in the long term.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site is accessible from the Oxfordshire Lorry Route Network. Access to the site must consider turning movements in and out of the site which may require new provision on the A415.

The highway network has severe capacity and congestion issues at peak times, especially at Frilfford lights junction and therefore increase in vehicular movements will be an issue.

Conclusion

The site is proposed as a potential new quarry within the Mineral Strategic Resource Area (Corallian Ridge – Oxford to Faringdon).

The site would have a moderate landscape or visual impact however the future restoration of the site has potential to deliver long term landscape character benefits. With appropriate mitigation, biodiversity is unlikely to pose a significant constraint. However, the site is within an area of considerable archaeological interest and whilst it has good access to the Oxfordshire Lorry Route Network, there is severe capacity and congestion issues on the local highway network. Allocation of this site would therefore only be appropriate if it could not be demonstrated that there were other more suitable sites to meet the requirement for soft sand.

SS-07 & CR-24: Home Farm, Shellingford

Site Information (as nominated in 2019) Site Location Home Farm, Shellingford Grid Reference SU317941 Administrative Area Vale of White Horse Parish Shellingford Site Nominee(s) Earthline Ltd Proposed Development Soft sand and Crushed rock (limestone) extraction. Potential new quarry. Site Area 39 ha Estimated annual 85,000tpa of soft sand output 50,000 tpa of crushed rock

Estimated Reserves Estimated total yield is 1mt of soft (including depth/ sand and 2 mt of crushed rock Estimated working depth of up to overburden) 15m Estimated overburden of 1.2m Proposed Restoration Agriculture and/or forestry and nature conservation uses to existing levels by the importation of inert waste. Opportunities for Geo- conservation. Access Existing access off A417. Proposed access off A417 or B4508. Estimated Unknown Traffic Movements Year of Land is freehold/owner occupied. Commencement Available within Local Mineral Plan period. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Areas for soft sand (Corallian Ridge – Oxford to Strategy – Strategic Resource Faringdon) and for crushed rock (East / South East of Faringdon) in the southern part of the Areas (Policy M3) county (Vale of White Horse). • Site is proposed as a potential new quarry. • Estimated total yield is 1mt of soft sand and 2 mt of crushed rock. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies within 250m of Shellingford Crossroads Quarry geological SSSI. (Policy C7) • Approximately1.7km from Wicklesham & Coxwell Pits SSSI; several other SSSIs within 5km. • The site lies adjacent to Ancient Woodland (AW) (Chaslins Copse 1.5ha) and (Withybed Copse – 1.6ha). The site also lies within 100m of AW (Kitemore Copse). • Site located in excess of 5km from International / European designated sites. • Site does not lie within 1km of a LNR or NNR. Landscape / Visual (Policy C8) • Site does not lie within 3km of an AONB. Water Environment and Flooding • Site is within flood zone 1. It is not within a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies within an area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies adjacent to Shellingford Conservation Area. • Historic England advise the potential impact on the setting of this Conservation Area should be taken into account in deciding whether or not this site, or part of it, is suitable for mineral extraction. • Site lies adjacent to a Grade II listed milestone. • Site lies within 150m of listed buildings in Shellingford. • There are currently no known archaeological constraints or historic landscape constraints. Transport and Access (Policy • Site lies adjacent to the Oxfordshire Lorry Route Network (A417). C10) • There are no areas of AM peak or PM peak traffic congestion identified in proximity to site. • The site lies within proximity to areas along the A417 with a history of ‘fatal’ and ‘serious’ RTIs. Public Rights of Way (Policy C11) • A public footpath runs adjacent to the western boundary of the site. Health and Amenity (Policy C5) • Site lies within 50m of residential dwellings to the west and north. • Site lies within 150m of residential dwellings to the west in in Shellingford. Green Belt (Policy C12) • Site does not lie within the Green Belt.

© Adams Hendry Consulting Ltd. 518 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Aerodrome Safeguarding (Policy • A small part of the site lies within the RAF Brize Norton buffer of airport safeguarding. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 4 existing minerals sites: Chinham Farm Quarry, Hatford Quarry, Faringdon Quarry and Shellingford Quarry. • Site lies within 3km of 4 nominated waste sites: 283 Hatford Quarry Stanford Ext, 229 Shellingford Quarry, 230 Chinham Farm and 281 Faringdon Quarry. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-08/CR-16, SS-12/CR-12, SS-15/CR-11, SS- 16/CR-21, SS-18/CR-22 and SS-19/CR-23.

Conclusion

The site does not operate as an existing minerals site and is proposed as a potential new quarry. The site is a greenfield site and appears to be in use for agricultural purposes and is within areas of Grade 3 BMV agricultural land. This is therefore a key consideration in promoting this site further for mineral development.

The site lies adjacent to the Oxfordshire Lorry Route Network (A417) and there is potential for access from the site directly onto the A417 Standford Road.

Consideration should also be provided to the residential dwellings which within close proximity to the site boundary, sufficient stand-off distance is likely to be required which may impact viability due to a reduction in the workable area.

For these reasons, the site is considered to have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource Limited borehole records available to assess quality. Borehole records within 400m of the site, to the east of the boundary indicates the presence of relatively large white limestone deposits which lie over significant deposits of yellow sand. Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no international designations within or adjacent to the site. It lies adjacent to several areas of irreplaceable habitat (ancient woodland) and there are other areas within 1km. Notable habitats include woodland along the southern boundary and there are several waterbodies within close proximity.

European protected species within or adjacent to the site include Great Crested Newt and several bat species in the local area. Records exist for several protected and notable mammal, bird, amphibian, plant and invertebrate species.

The site lies adjacent to Chaslins Copse Local Wildlife Site (LWS) and partially within the West Oxon Heights, Streams, Hills, Woods and Parks (Conservation Target Area) CTA.

Overall the potential ecological impacts of the proposals are likely to be high. The site is large and in close proximity to several known sensitive ecological receptors.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It is nominated as a new large allocation characterised by two large intensively farmed arable fields. Hedgerow boundaries are largely absent within the site but still exist near roads in places. A woodland belt following a stream defines the western and southern boundaries of the site.

© Adams Hendry Consulting Ltd. 520 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 The site is approximately 70m from Shellingford settlement / conservation area and separated from it by a woodland belt.

There is a history of mineral workings in the wider area. Site is expected to have a moderate effect on the local landscape character.

A Pubic Right of Way runs along the western boundary of the site with views into the site. Occasional views from adjacent roads into the site are possible. Mitigation in the form of native planting, hedgerow enhancements and bunding could assist in mitigating visual impacts.

This is a large new site in an area that is already subject to several existing and proposed mineral sites. Overall the site is expected to moderately affect both landscape character and views due to introducing mineral extraction into an agricultural landscape of moderate sensitivity and by causing moderate impacts on public views. Restoration has potential to deliver landscape enhancements in the long term

This site is only one of several sites in this area that is being proposed for mineral workings and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

The site lies adjacent to the A417, a strategic route known to have capacity issues in the peaks.

If the site is accessed from the B4508, HGVs would turn left towards the A417.

Conclusion

The site lies within Mineral Strategic Resource Areas for soft sand and crushed rock and is adjacent to the A417 on the Oxfordshire Lorry Route.

The site has been nominated as a potential new site. Core Strategy Policy M4 makes it clear that the priority is for the extension of existing quarries rather than new sites.

The ecological impacts of extraction are anticipated to be high given the site’s proximity to sensitive ecological receptors. The site is a large site in an area with a number of existing mineral workings and therefore extraction is likely to have a moderate effect on landscape character and public views.

Site SS-08 & CR-16: Shellingford Quarry (Western Extension)

Site Information (as nominated in 2018) Site Location Shellingford Quarry Western Extension Grid Reference SU324935

Administrative Area Vale of White Horse Parish Shellingford Site Nominee(s) Multi-Agg Limited

Proposed Development Soft sand and Crushed rock extraction. Extension to Shellingford Quarry. Site Area 37 ha

Estimated annual 100-150,000 tpa output Estimated Reserves Estimated total yield of 2.7 mt soft (including depth/ sand. Estimated total yield of 1.9 mts of overburden) crushed rock. Estimated working depth of 16m Estimated overburden of 1.2m Proposed Restoration Agriculture and nature conservation.

Access Existing quarry access onto A417 Stanford Road. Estimated As existing Traffic Movements Year of As soon as planning permission is Commencement granted and other necessary permissions / licences are in place. Lifetime of Less than 1 year for remaining Operation permitted reserves.

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • The majority of the site (except the southern tip of the site adjacent to Baulking Lane) lies Strategy – Strategic Resource within the Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Oxford to Areas (Policy M3) Faringdon) and for crushed rock (East / South East of Faringdon) in the southern part of the county (Vale of White Horse). • Site is proposed as an extension to Shellingford Quarry. • Estimated Site yield 2.7 mt soft sand and 1.9 mt crushed rock District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies within 165m of Shellingford Crossroads Quarry SSSI. (Policy C7) • Site lies within 260m of Ancient Woodland (Withybed Corpse). • Site located in excess of 5km from International / European designated sites. • Site is not located within 1km of an LNR or NNR. • The adjacent Shellingford Quarry is a Local Geological site Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site is not within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site is not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within an area of Grade 3 BMV agricultural land. Historic Environment (Policy C9) • Site lies within 300m of a number of listed buildings to the west in Shellingford. • Site lies within 250m of Shellingford conservation area. • Site is within area of considerable archaeological potential. There are however currently no known heritage assets within the site. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies adjacent to the Oxfordshire Lorry Route Network (A417). C10) • Transport movements associated with the site would be as per the existing Shellingford Quarry operation. The site will use the existing access onto the A417 Stanford Road. • There are no areas of AM peak or PM peak traffic congestion identified in proximity to site.

524 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • The site lies adjacent to an area along the A417 with a history of a ‘fatal’ RTI and also within proximity to areas with a history of ‘serious’ RTI’s. Public Rights of Way (Policy C11) • A public footpath lies adjacent to the southern boundary of the site. Health and Amenity (Policy C5) • Site lies opposite a residential property to the north at the junction of the A417 and B4508. • Site is adjacent to the White Horse Business Park at the south east boundary. • Site is adjacent to Church Farm to the immediate west of the site. • Site lies approximately 250m from residential dwellings to the south west of Shellingford, including a Primary School. Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site does not fall within an aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 4 existing minerals sites: Shellingford Quarry, Chinham Farm Quarry, Hatford Quarry and Faringdon Quarry. • Site lies within 3km of 4 nominated waste sites: 283 Hatford Quarry Ext, 229 Shellingford Quarry, 230 Chinham Farm and 281 Faringdon Quarry. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-07/CR-24, SS-12/CR-12, SS-15/CR-11, SS- 16/CR-21, SS-18/CR-22 and SS-19/CR-23.

Conclusion The site does not operate as an existing minerals site and is a potential extension to the existing site at Shellingford Quarry. The site is a greenfield site and appears to be in use for agricultural purposes and is within areas of Grade 3 agricultural land.

The site lies adjacent to the Oxfordshire Lorry Route Network (A417) and it is likely that the existing Shellingford Quarry access onto the A417 Stanford Road would be used.

Potential impacts on the amenity of residential dwellings adjacent to and within close proximity to the site boundary, including the primary school in Shellingford will require further consideration. A sufficient stand-off distance is likely to be required which may reduce the workable area and impact the site’s viability.

For these reasons, the site is considered to have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Quarrying of sand and limestone and restoration by infill with inert waste at the existing Shellingford Quarry was originally permitted in 1986. The current quarrying operations were permitted on 27.08.2009, MW.0132/09.

‘Storage and exportation of sorted inert material’ (including recycling of inert waste to produce secondary aggregate for sale off site) permitted 08.10.2009, MW.0161/09; proposed throughput 60,000 tpa. Conditions required: • No aggregates to be imported to site after completion of sand extraction or by 31.12.2019, whichever is earlier; • Site to be restored within one year of completion of mineral extraction and landfill or by 31.12.2021, whichever is earlier. This is the currently active permission for recycling at Shellingford Quarry.

Permission MW.0132/09 for quarrying and infill was varied by a new permission granted on 28.04.2011, MW.0020/11. This is the current operative permission for the quarry. Conditions require: Cessation of mineral extraction and deposit of waste by 31.12.2028; and completion of restoration of the site by 31.12.2029; Access only via existing quarry access onto the A417; HGV movements limited to 200 per day (100 in, 100 out).

An eastern extension to Shellingford Quarry was also permitted on 28.04.2011, MW.0021/11. Conditions require: Cessation of mineral extraction and deposit of waste by 31.12.2020; and completion of restoration of the site by 31.12.2021; Access only via existing quarry access onto the A417; HGV movements limited to 200 per day (100 in, 100 out).

The eastern extension area has been worked out and remaining mineral reserves in the main quarry area are low; the site promotor states that there is less than one year of available reserves.

© Adams Hendry Consulting Ltd. 526 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 m3 of inert waste. The existing quarry access to the A417 and the processing plant within the existing quarry are proposed to be used (subject to a separate application for retention of the plant etc being submitted and approved). The Council’s Planning and Regulation Committee on 15.07.2019 resolved that, subject to legal agreements on long term aftercare and lorry routeing, permission be granted for this application.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Limited borehole records available to assess quality. Borehole records available within 300m to the east of the southern area of the site show significant depths of Oxford clay and clayey sand deposits. Poor.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no international designations within or adjacent to the site.

Local designations include Chaslins Copse local wildlife site, approximately 500m away. The site is also partially covered by the local designation West Oxon Heights Streams, Hills, Woods and Parks Conservation Target Area (CTA).

The site is within 200m of irreplaceable ancient woodland, and several other areas of ancient woodlands are within 1km of the site. Other nearby woodlands and waterbodies are also listed as notable habitats.

Records for European protected species include Great Crested Newts and several bat species in the local area. Other protected and notable species within and adjacent to the site include several mammals, birds, amphibians, plants and invertebrates.

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It is nominated as a large extension to Shellingford Quarry in gently rolling landscape that will result in loss of intensively farmed fields. Hedgerow boundaries are largely absent giving a sense of openness in the southern part of the site. Some established hedgerows still exist in the north western part of site. Northern part considered more sensitive in landscape character terms.

There would be occasional views from roads (Fernham Road, A415), the Public Right of Way (PRoW) and business park. Shellingford is largely screened by a woodland belt and there is no direct footpath link to settlement. Impact on public views limited but will depend on timing, ie restoration of existing quarry and workings of extension. Mitigation in the form of native planting and bunding will assist in mitigating visual impacts.

Piecemeal enclosures are historic parts of the landscape and sensitive to development

© Adams Hendry Consulting Ltd. 527 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Restoration has potential to deliver landscape enhancements in the long term.

Overall this expansion is expected to moderately affect the landscape character and views by introducing mineral extraction into this rural landscape in close proximity to Shellingford conservation area. The impact will be influenced by timing of work in relation to restoration of existing quarry and start/phasing of working.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

A417 is a strategic route and is known to have capacity issues in the peaks.

Existing access appears acceptable.

Conclusion

The majority of the site lies within Mineral Strategic Resource Areas for soft sand and crushed rock. It lies adjacent to the Oxfordshire Lorry Route Network (A417) and it is likely that the existing Shellingford Quarry access onto the A417 Stanford Road would be used.

The site is in close proximity to a number of sensitive ecological receptors and the expansion of Shellingford Quarry is expected to moderately affect the landscape character and views by introducing mineral extraction into this rural landscape in close proximity to Shellingford conservation area.

Current planning application MW.0104/18 proposes mineral extraction and infilling with imported inert materials within most of the area of the nominated site as a western extension to the existing Shellingford Quarry. The Council’s Planning and Regulation Committee resolved to approve the application in July 2019 subject to legal agreements on long term aftercare and lorry routing.

Site SS-12 & CR-12: Land at Chinham Farm (Chinham Hill)

Site Information (as nominated in 2009) Site Location Land at Chinham Farm (Chinham Hill) Grid Reference SU314952 Administrative Area Vale of White Horse Parish Shellingford Site Nominee(s) Hills Quarry Products Ltd Proposed Development Soft sand extraction. Crushed rock extraction. Extension to Bowling Green Farm Quarry. Site Area 8 ha Estimated annual Unknown output Estimated Reserves Estimated yield of 0.3mt Sand (I&O (including depth/ 2018) Estimated yield of 0.1mt Crushed rock overburden) (I&O 2018) Estimated working depth of 10m Estimated overburden of 0.3m Proposed Restoration Agriculture and amenity Access Existing access to Bowling Green Farm Quarry off A417 Estimated As existing Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation Previous permission for extraction at this site has lapsed; Current permission MW.0124/16 for adjacent Chinham Farm site requires cessation of extraction by 31/12/2037

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Area for crushed rock (East / South East of Strategy – Strategic Resource Faringdon) and soft sand (Corallian Ridge area from Oxford to Faringdon) in the southern part Areas (Policy M3) of the county (Vale of White Horse). • Site is proposed as an extension to Bowling Green Farm Quarry. • The total yield for the site is estimated at 0.3mt soft sand and 0.1mt crushed rock. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site located in excess of 5km from International/European designated sites. (Policy C7) • An area of ancient woodland lies approximately 75m to the north • Shellingford Crossroads Quarry SSSI lies approximately 1.3km to the south east. • Site located in excess of 1km from NNR and protected species. • Site located in excess of 500m from a SINC or LNR. Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within flood zone 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies within predominately Grade 2 agricultural land with a small area of Grade 3 at the northern end of the site. Historic Environment (Policy C9) • Historic England advise the site lies opposite the Faringdon Conservation Area (approximately 1.4km to the west) and is potentially within the setting of the Earthwork in Ewedown Copse Scheduled Monument approximately 690m north east of the site. • Wadley House and Wadley Lodge Farmhouse are the Grade II Listed buildings approximately 700m to the north west. • The site is located in an area of considerable archaeological interest. Limited archaeological investigations have recorded the presence of a Romano British settlement and possible Villa to the west of the allocation. Its full extent and character have not been fully understood. Evidence of field systems, probably relating to the settlement, have been recorded to the south of the allocation. Transport and Access (Policy • The site could potentially use the existing access to Bowling Green Farm quarry which links C10) directly to the Oxfordshire Lorry Route Network (A417). • There are no areas of AM or PM peak traffic congestion identified in proximity to site. • There are areas with a history of ‘serious’ and ‘fatal’ RTIs within 2km of the site. Public Rights of Way (Policy C11) • A public footpath runs east-west approximately 125m to the north of the site.

© Adams Hendry Consulting Ltd. 531 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Health and Amenity (Policy C5) • Site lies within 225m of residential dwellings at Chinham Farm to the south east of the site, Bowling Green Cottages 300m to the south and Bowling Green Farm 800m to the west Green Belt (Policy C12) • Site is not located in the Green Belt. Aerodrome Safeguarding (Policy • Site lies within the RAF Brize Norton aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 4 existing minerals sites: Chinham Farm Quarry, Hatford Quarry, Shellingford Quarry and Faringdon Quarry. • Site lies within 3km of 4 nominated waste sites: 283 Hatford Quarry Ext, 229 Shellingford Quarry, 230 Chinham Farm and 281 Faringdon Quarry. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-07/CR-24, SS-08/CR-16, SS-15/CR-11, SS- 16/CR-21, SS-18/CR-22 and SS-19/CR-23.

Conclusion

The site was nominated in 2009, so there is uncertainty as to whether the site is still available.

The site does not operate as an existing minerals site but could be a potential extension to the existing Bowling Green Farm Quarry. The site is a greenfield site and appears to be in use for agricultural purposes. The site area is relatively small at 8 hectares.

The site has access to the Oxfordshire Lorry Route Network (A417), assuming the existing site access to Bowling Green Farm quarry can be used.

Potential impacts on historic assets and local amenity will need further consideration in deciding whether or not this site, or part of it, is suitable for mineral extraction.

The site is however considered to have some potential as a mineral working site for crushed rock and soft sand and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Permission was granted on 26.05.2011, MW.0132/10 for extraction of sand and restoration to agriculture at Chinham Hill (the nominated site) as an extension to the Bowling Green Farm/Chinham Farm Quarry. This application was for the extraction of 300,000 tonnes of sand at an average rate of 50,000 tpa over 6 years. This permission was not commenced within 5 years of the permission date and it has therefore lapsed.

Quarrying at Bowling Green Farm was originally permitted on appeal on 12.08.1987, MW.010/87 (APP/U3100/A/86/53698). There have since been a number of further permissions for quarrying at Bowling Green Farm and the adjacent Chinham Farm, as extensions to the original quarry, using the same access from the A417.

The earlier permissions have been worked out and the currently operative permission is MW.0124/16, granted 16.06.2017 for the extension of quarry (at Chinham Farm) with extraction of sand and limestone and restoration to agriculture including using existing quarry infrastructure at Bowling Green Farm Sandpit. Conditions require cessation of mineral extraction by 31.12.2037 and restoration by 31.12.2038.

This permission is for the extraction of 1.5 mt of sand and 0.6 mt of limestone; and infilling with 950,000 m3 of inert waste. Most of the permitted mineral reserve has yet to be worked. The applicant estimated annual production of 80,000 tonnes of sand and 15,000 tonnes of limestone, with annual importation of 60,000 m3 of inert waste for restoration. It is estimated that mineral working will continue beyond the end of the period covered by the Minerals and Waste Local Plan (i.e beyond the end of 2031).

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Data not available.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within the site, however an area of ancient woodland (Chinham Copse) lies within 100m of the site to the north. Notable habitats include deciduous woodland to the south of the site and several nearby waterbodies. Frogmore Brook is within 100m of the site to the north.

European protected species in the area include Great Crested Newts and bats. Numerous records exist for protected and notable species of mammal, bird, amphibian, plant and invertebrates.

The site lies adjacent to West Oxon Heights Streams, Hills, Woods and Parks Conservation Target Area (CTA). The closest Local Wildlife Site (LWS) is Chaslins Copse, approximately 1.1km to the south.

Overall the site itself is small and therefore likely impacts could be considered moderate.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. The site is proposed as an extension to an existing quarry. It includes a small woodland copse with waterbodies at its southern end which are likely to be affected. Hedgerow boundaries are largely absent creating a sense of openness. Development is likely to result in loss of characteristic vegetation and features (e.g. woodland copse, mature trees/scrub)

Views from Public Rights of Way are expected to be limited due to intervening vegetation. Occasional views from the A415 will exist but the site will be viewed in the context of the existing quarry. There will be views from a low number of properties, however the visibility of the site in public views is limited. Mitigation in the form of native planting and bunding is likely to assist in mitigating visual impacts.

Overall the site is considered to cause a moderate impact on landscape character due to the likely loss of characteristic landscape features such as the small woodland copse at the southern end of the site. The retention of this could potentially reduce the impact. Impacts on public views will be limited and mitigatable. Restoration has the potential to deliver enhancements in the long term.

Compliance with Policy C10: Transport - Highways Officer Assessment

The A417 is a strategic route known to have capacity issues in the peaks.

The use of the existing access is considered acceptable in principle; however, enhancements are likely to be required.

Conclusion

The site lies within the Mineral Strategic Resource Area for crushed rock and soft sand and is proposed as an extension to Bowling Green Farm Quarry. It has access to the Oxfordshire Lorry Route Network (A417) utilising the existing access to Bowling Green Farm quarry.

Impacts on ecology are considered to be moderate particularly given the small size of the site. Development of the site is likely to cause a moderate impact on landscape character due to the loss of characteristic features.

Planning permission was granted for the extraction of sand as an extension to the Bowling Green Farm/Chinham Farm Quarry in 2011, however this was not implemented and the permission has now lapsed.

© Adams Hendry Consulting Ltd. 534 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 There are a number of existing and nominated mineral and waste sites within 3km of the site and therefore cumulative impacts will need to be considered taking into account the overall requirement for crushed rock and soft sand over the plan period set out in the Core Strategy.

Site SS-15 & CR-11: Hatford Quarry North Extension

Site Information (as nominated in 2018) Site Location Hatford Quarry North Extension Grid Reference SU333957 Administrative Area Vale of White Horse Parish Hatford Site Nominee(s) Hatford Quarry Ltd Proposed Development Soft sand extraction. Crushed rock extraction. Extension to Hatford Quarry. Site Area 42 ha Estimated annual 150,000 tpa – includes both soft output sand and crushed rock. Estimated Reserves Estimated total yield 0.5 mt soft (including depth/ sand Estimated total yield 1.5 mt overburden) crushed rock Estimated working depth of 10m Estimated overburden of 2m Top layers of sand were previously worked before 1990. Proposed Restoration Low level restoration to agriculture. Access Existing access onto Sandy Lane, with mineral transported via the existing quarry access onto the B4508 Fernham Road. Estimated As existing. HGV movements Traffic would comply with existing permission. Movements Year of As soon as planning permission is Commencement granted, and other necessary permissions /licences are in place. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within the Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Strategy – Strategic Resource Oxford to Faringdon) and for crushed rock (East / South East of Faringdon). Areas (Policy M3) • The site is located in the southern part of the county (Vale of White Horse). • Site is proposed as an extension to Hatford Quarry. • Estimated total yield is 0.5 mt tonnes of soft sand and 1.5mt of crushed rock. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Hatford Sand Pit Local Geological Site adjoins the site to the south. (Policy C7) • Site lies within approximately 360m of Buckland Warren SSSI to the north east and Shellingford Crossroads Quarry SSSI lies approximately 1.5km to the south. • Site located in excess of 500m from a SINC or LNR. • Site located in excess of 5km from International / European designated sites. Nearest SAC is Hackpen Hill, approximately 10km south of the site. • The site lies adjacent to ancient woodland Landscape / Visual (Policy C8) • Site is not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Approximately 80% of the site is Grade 2 agricultural land with the remainder Grade 3. Historic Environment (Policy C9) • Site lies within 500m of Hatford conservation area and a number of listed buildings in Hatford. • Scheduled Monument located within 1.4km of the site. • The site is located in an area of considerable archaeological interest. In the north western part of the allocation is an extensive spread of cropmarks. These features include linear features and a substantial enclosure with a possible trackway and entrance on the western side. These features have not yet been dated but are likely to be of later prehistoric and/or Romano British origin.

© Adams Hendry Consulting Ltd. 538 January 2020 Oxfor dshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • In the 1970s and 80s some limited excavation was undertaken in the southern end of the allocation which recorded archaeological features related to a small Roman settlement. It is unclear currently how extensive these excavations were. • There are no known historic landscape constraints. Transport and Access (Policy • Site lies approximately 1.2km from the A420 on the Oxfordshire Lorry Route Network and C10) approximately 2.2km from the A417 (via the B4508). • There are no areas of AM or PM peak traffic congestion identified in proximity to site. • Site does not lie within close proximity to areas with history of RTIs. Public Rights of Way (Policy C11) • A public bridleway runs along the northern boundary of the site and partially along the southern boundary. Health and Amenity (Policy C5) • A residential dwelling is located approximately 40m from the northern boundary and 120m from the southern boundary. Green Belt (Policy C12) • Site does not lie within Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton buffer of airport safeguarding. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • There are 3 existing minerals sites within 3km of the site: Hatford Quarry, Shellingford Quarry and Chinham Farm. • Site lies within 3km of 3 nominated waste sites: 283 Hatford Quarry Stanford Ext, 229 Shellingford Quarry and 230 Chinham Farm. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-07/CR-24, SS-08/CR-16, SS-12/CR-12, SS- 16/CR-21, SS-18/CR-22 and SS-19/CR-23.

Conclusion

The site is proposed as a potential extension to the existing site at Hatford Quarry. It is a greenfield site and appears to be in use for agricultural purposes within areas of best and most versatile agricultural land. The site lies within 1.2km of the Oxfordshire Lorry Route Network (A420).

Consideration would need to be given to the residential dwellings which lie within close proximity to the site boundary.

The site is considered to have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

The nominated site was previously worked for sand, from the upper layers of the land, prior to 1990, and restored at a lower level. The existing Hatford Quarry is to south of site, on the opposite side of Sandy Lane. Quarry access road runs through this site to B4508. The currently operational planning permission for mineral extraction at Hatford quarry is:

No publicly available information on remaining permitted reserves; assume will be worked out by current permission end date.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on site indicate shallow deposits of Red Down Sand extending to depths of 1.5m. Further borehole records taken 700m to the south of the site adjacent to the B4508 indicate the presence of significant white and soft limestone and grey sand deposits. Fair-Good

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Irreplaceable habitats within and adjacent to the site include several ancient woodlands, within 1km. Peat Bottom Wood ancient woodland and Rabbit Hill ancient woodland are the two closest, within 50m of the site. Other notable habitats in close proximity to the site include woodlands, pastures and waterbodies.

The presence of Great Crested Newts has been recorded in the area, alongside several bat species, both of which are protected under European law. Other protected and notable species within and adjacent to the site include several mammals, birds, amphibians, plants and invertebrates.

The site is within the West Oxon Heights Streams, Hills, Woods and Parks Conservation Target Area (CTA) and adjacent to Buckland Warren Woods Local Wildlife Site (LWS).

The site is adjacent to several sensitive ecological receptors, notably the Buckland Warren Woods LWS with areas of ancient woodland. Overall the potential ecological impacts of the proposals are likely to be high.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It is a very large site that comprises several large intensively farmed fields and a small copse of woodland/ scrub on gently sloping terrain, adding interest.

Sandy Lane, a single-track lane in a tranquil area, and associated mature vegetation forms the southern boundary and separates the site from the existing quarry such that the site might not be perceived as an extension but as a new quarry. There are some hedgerows towards the north western end of the site.

There would be views from the two Public Rights of Way. Large parts of the site are not readily visible from public vantage points. There would be occasional views from Sandy Lane, Carswell Golf and Country Club. Views from The Hideaway (residential properties) would also be affected.

Sandy Lane is partly screened by rows of conifers which are uncharacteristic elements in the landscape. The eastern part of the site is lower lying and more hidden from views from Sandy Lane. The western part is considered visually more sensitive. Mitigation in the form of native planting and bunding is likely to assist in mitigating visual impacts.

Overall the landscape and visual impact is considered to be moderate, however, the level of impact will depend on the phasing of workings and restoration of existing and proposed sites. Simultaneous working in the area has the potential to result in substantial effects on the landscape character and views.

Restoration has the potential to deliver landscape and visual benefits in the long-term.

The cumulative impact of the various developments in the area need to be considered.

Compliance with Policy C10: Transport - Highways Officer Assessment

The A420 is a strategic route and is known to have capacity issues in the peaks.

Existing access stated to be designed to appropriate standard.

The site lies within Mineral Strategic Resource Areas for soft sand and crushed rock and lies approximately 1.2km from the A420 on the Oxfordshire Lorry Route Network

The site is nominated as an extension to Hatfield Quarry which has permission for the extraction of limestone and sand until 2020/21 with restoration to be completed by September 2021.

The site is adjacent to several sensitive ecological receptors and therefore the potential ecological impacts of the proposals are likely to be high. The landscape and visual impact is considered to be moderate.

Site SS-16 & CR-21: Hatford Quarry Stanford Extension

Site Information (as nominated in 2018) Site Location Hatford Quarry Stanford Extension

Grid Reference SU335942

Administrative Area Vale of White Horse

Parish Stanford in the Vale

Site Nominee(s) Hatford Quarry Ltd

Proposed Development Soft sand and Crushed rock extraction. Extension to Hatford Quarry. Site Area 27 ha Estimated annual 150,000 tpa output Estimated Reserves Estimated total yield of 3.5 mt soft (including depth/ sand Estimated total yield of 2 mt overburden) Crushed rock Estimated working depth of 18m. Estimated overburden of 1.2m Proposed Restoration Agriculture, woodland and wetlands.

Access Access from B4508 Fernham Road

Estimated As for existing quarry. Traffic Movements Year of Not before 2030. Commencement Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Oxford Strategy – Strategic Resource to Faringdon) and for crushed rock (East / South East of Faringdon), in the southern part of the Areas (Policy M3) county (Vale of White Horse). • This is a greenfield site proposed as a potential extension to Hatford Quarry. • Estimated total yield of 3.5 mt soft sand and 2 mt crushed rock. District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies approximately 550m from Shellingford Crossroads Quarry SSSI. (Policy C7) • Site located in excess of 5km from International / European designated sites. The nearest SAC is Hackpen Hill, approximately 9.5km south of the site. • Site not within or adjacent to ancient woodland. • Site located in excess of 500m from a SINC or LNR. • Shellingford Quarry, a Local Geological Site is approximately 250m to the south west of the site. Landscape / Visual (Policy C8) • Site is not located within an AONB. Water Environment and Flooding • Site not within flood zones 2 or 3 or a source protection zone. (Policy C3 and Policy C4) • Site adjacent to a flood zone 3 area. • Proposed site use would be water compatible. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Site within area of Grade 3 agricultural land. Historic Environment (Policy C9) • Site lies within 250m of the Hatford Conservation Area and within 300m of Stanford in the Vale Conservation Area. • There are 6 listed buildings approximately 300m north of site in Hatford. • Numerous listed buildings over 300m away in Stanford in the Vale. • Archaeological recording to the south of the site did not record any significant archaeological features. There are therefore no known archaeological constraints. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies within 1km of the A417 Oxfordshire Lorry Route. C10) • Site connects to the A417 Oxfordshire Lorry Route via the B4508 (Fernham Road), The B4508 passes two residential dwellings, one of which is located on the junction with the A417. • No AM peak or PM peak traffic congestion identified within proximity to site. • Site lies 1km from a fatal RTI on the A417 and within 3km of three serious RTIs (2 on the A417 and 1 on the B4508).

© Adams Hendry Consulting Ltd. 545 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Public Rights of Way (Policy C11) • Public bridleway runs adjacent to western side of the site and further footpath runs along within 100m of the north east boundary of the site. Health and Amenity (Policy C5) • Residential dwelling lies 40m to the east of the site. • Dwellings in Hatford are approximately 300m from the site, as are dwellings in Stanford in the Vale. Green Belt (Policy C12) • Site does not lie within the Green Belt. Aerodrome Safeguarding (Policy • Site does not lie within an aerodrome safeguarding area. M10)

Potential Cumulative Impact • Site lies within 3km of three existing waste sites: Shellingford Quarry, Chinham Farmand Stanford in the Vale (minerals and waste sites) HWRC. • Site lies within 3km of three existing minerals sites: Chinham Farm Quarry, Hatford Quarry and Shellingford Quarry. • Site lies within 3km of three nominated waste sites: 229 Shellingford Quarry, 230 Chinham Farm and 283 Hatford Quarry Stanford Ext. • Site lies within 3km of seven nominated minerals sites: SS-03/CR-17 Hatford Quarry, South extension, SS-07/CR- 24 Home Farm, SS-08/CR-16 Shellingford Quarry Western extension, SS-12/CR-12 Land at Chinham Farm (Chinham Hill), SS-15/CR-11 Hatford Quarry North extension, SS-18/CR-22 Hatford Quarry West extension and SS-19/CR-23 Home Farm Carswell.

Conclusion

The site lies within the Mineral Strategic Resource Area in the southern Oxfordshire area and is a potential greenfield extension to the existing Hatford Quarry. The site is located on Grade 3 agricultural land and the sites restoration proposals would need to subject to scrutiny at the detailed assessment stage. Residential properties lie in close proximity to the site the potential impact on which will need to be considered further.

Given the site’s location within the Mineral Strategic Resource Area and the connectivity with the Oxfordshire Lorry Route, this site will be carried forward to further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

Existing Hatford Quarry is to north east of site, on north side of B4508. Existing quarry access is on opposite (north) side of B4508. The currently operational planning permission for mineral extraction at Hatford quarry is:

No publicly available information on remaining permitted reserves; assume will be worked out by current permission end date.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Borehole records on site indicate the presence of limestone deposits which overlie significant levels of grey and yellow sands with limited amount of overburden. Good.

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

There are no irreplaceable habitats within or adjacent to the site. Frogmore Brook along the eastern boundary and adjacent woodlands are recorded as notable habitats.

Great Crested Newts and several bat species have been recorded in the local area, both of which are protected under European law. Other protected and notable species within and adjacent to the site include several mammals, birds, amphibians, plants and invertebrates. Part of site within West Oxon Heights Streams, Hills, Woods and Parks CTA. Chaslins Copse LWS approx 1.7km to west.

Overall the ecological impacts of the proposals are likely to be low to moderate. No significant impacts on any statutory site of nature conservation interest are anticipated however the site is partly within a CTA.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. It is a new large site that will result in the loss of several fields or semi-improved grassland on gently undulating topography. The low / gappy hedgerow increases inter-visibility and gives a sense of openness. Despite the proximity of the A417, it is a tranquil area. In landscape terms this site is likely to be perceived as new site rather than as an extension.

The site is located approximately 250m from Stanford in the Vale settlement and conservation area and approximately 150m from Hatford settlement and conservation area. Development will impact on views from Stanford in the Vale and Hatford settlements /conservation areas.

A PRoW runs along the western boundary. The Vale Way passes the site in short distance to the east.

Overall this site nomination is expected to substantially affect the landscape character and views due to its large size, its detached nature and because it will introduce intrusive mineral extraction into the rural countryside and in close proximity to two settlements and conservation areas.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

B4508 Fernham Road and its suitability for additional HGV movements need to be assessed due to width of road width and condition.

Conclusion

The site lies within Mineral Strategic Resource Areas for soft sand and for crushed rock and within 1km of the A417 Oxfordshire Lorry Route.

Allocation of the site for is likely to have an adverse impact on landscape character and on sensitive visual receptors. It also has the potential to affect the Stanford in the Vale and Hatford Conservation Areas.

Site SS-18 & CR-22: Hatford Quarry West Extension

Site Information (as nominated in 2018) Site Location Hatford Quarry West Extension Grid Reference SU323958

Administrative Area Vale of White Horse

Parish Hatford

Site Nominee(s) Hatford Quarry Ltd

Proposed Development Soft sand and Crushed rock extraction. Extension to Hatford Quarry. Site Area 19 ha

Estimated annual up to 150,000 tpa output Estimated Reserves Estimated total yield of 0.2 mt soft (including depth/ sand Estimated total yield of 1.2 mt overburden) crushed rock. Estimated working depth of 5-12m Estimated overburden of 1.2m Proposed Restoration Low level restoration to agriculture. Access Existing quarry access onto B4508 Fernham Road. Estimated As existing. Traffic Movements Year of As soon as planning permission is Commencement granted, and other necessary permissions / licences are in place. Lifetime of Unknown Operation

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Oxford Strategy – Strategic Resource to Faringdon) and for crushed rock (East / South East of Faringdon) in the southern part of the Areas (Policy M3) county (Vale of White Horse). • Site is proposed as a potential extension to Hatford Quarry. • Estimated site yield is 0.2mt of soft sand and 1.2 mt crushed rock District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Site lies within 200m of Ancient Woodland (Brickkiln Copse). (Policy C7) • Site lies approximately 800m from the Buckland Warren SSSI to the north east of the site. • Site does not lie in close proximity to any LNR’s or NNR’s. • Site located in excess of 5km from International / European designated sites. Nearest SAC is Hackpen Hill, approximately 10km south of the site. Landscape / Visual (Policy C8) • Site not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within a flood zone or source protection zone. (Policy C3 and Policy C4) • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site does not lie in close proximity to an AQMA. Soil Resources (Policy C6) • Site lies within an area of predominantly Grade 2 and 3 agricultural land. Historic Environment (Policy C9) • Site lies within 1.5km of Hatford conservation area and a number of listed buildings in Hatford. • Scheduled Monument located within 300m of the site. • The site is located in an area of considerable archaeological interest. Archaeological recording in the current extraction area immediately east of the allocation has revealed evidence of later prehistoric and Romano British activity and settlement. This clearly extends into the allocation area. • There are currently no known historic landscape constraints. Transport and Access (Policy • Site lies approximately 3km from A417 part of the Oxfordshire Lorry Route via Sandy Lane (a C10) single carriage way road) and Hatford on the B4508. • Alternative access is to the A420, 1.3km from the site at its closest point via Sandy Lane and Barcote Lane (single carriageway roads). • There are no areas of AM or PM peak traffic congestion identified in proximity to site. • Site does not lie within close proximity to areas with history of RTIs. Public Rights of Way (Policy C11) • A public bridleway runs adjacent to the site to the north. • The Vale Way can be found some distance to the south along Frogmore Brook. Health and Amenity (Policy C5) • Site lies adjacent to two residential dwellings immediately to north east and north west of the site boundary.

© Adams Hendry Consulting Ltd. 551 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 Green Belt (Policy C12) • Site does not lie within Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton buffer of airport safeguarding. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 3 existing minerals sites: Chinham Farm Quarry, Hatford Quarry and Shellingford Quarry. • Site lies within 3km of 3 nominated waste sites: 283 Hatford Quarry Stanford Ext, 229 Shellingford Quarry and 230 Chinham Farm. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-07/CR-24, SS-08/CR-16, SS-12/CR-12, SS- 15/CR-11, SS-16/CR-21 and SS-19/CR-23.

Conclusion

The site does not operate as an existing minerals site and is a potential extension to the existing site at Hatford Quarry. The site is a greenfield site and appears to be in use for agricultural purposes.

The site lies within 3km of the Oxfordshire Lorry Route Network (A417 and A480).

Potential adverse impacts on residential dwellings adjacent to the north of the site and on best and most versatile agricultural land will need to be further assessed and a sufficient stand-off distance is likely to be required which may reduce the workable area and impact viability.

Notwithstanding these constraints, the site is considered to have some potential as a mineral working site for crushed rock and will be subject to detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Existing Hatford Quarry is to east of site. Quarry access road runs through this site to B4508. The currently operational planning permission for mineral extraction at Hatford quarry is:

No publicly available information on remaining permitted reserves; assume will be worked out by current permission end date.

A planning application is expected to be submitted for the nomination site. A request for an EIA Scoping Opinion has been submitted, MW.0050/18; the Council’s opinion was given on 06.07.2018. The scoping request stated that the extension area is expected to yield 0.2 mt of sand and 1.2 mt of limestone; and at current rates of extraction and processing, it is anticipated that it would take 8 years to complete extraction.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

The closest irreplaceable habitat is the ancient woodland, Peat Bottom Wood, approximately 430m to the east of the site. Notable habitats adjacent to the site include Long Plantation deciduous woodland.

The presence of Great Crested Newts and several bat species have been recorded in the area, both of which are protected under European law. Other protected and notable species within and adjacent to the site include several mammals, birds, amphibians, plants and invertebrates.

The site lies immediately adjacent to West Oxon Heights Streams, Hills, Woods and Parks Conservation Target Area (CTA). Buckland Warren Woods Local Wildlife Site lies approximately 680m to the east.

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

The site is not within a designated landscape or its setting. It is proposed as an extension to Hatford quarry which would result in the loss of some intensive farmland. The site adjoins the existing quarry and is bounded to the west by Long Plantation. It is a tranquil area that feels remote.

The impact on local landscape is considered to be moderate subject to existing mature boundary vegetation being retained. Restoration has the potential to enhance landscape character in the long term.

Development will be viewed in context of existing quarry and will impact on views from residential dwellings adjacent to the site. Mitigation planting or bunding will assist in reducing visual impacts from properties and public right of ways.

Overall this allocation is expected to have a minor effect on the local landscape character and views due to the site’s location next to the existing quarry, the partially screened nature of the site and the lack of impact on settlements / conservation areas. Visual impacts are expected to be moderate but partly mitigatable during operation.

The temporary nature of the development offers potential for landscape enhancements in the long term.

This site is one of several sites in this area that is being proposed for mineral and/or waste treatment and cumulative impacts should be assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

B4508 Fernham Road and its suitability for additional HGV movements need to be assessed due to width of road width and condition.

Conclusion

The site lies within Mineral Strategic Resource Areas for soft sand and for crushed rock and is approximately 3km from the A417 part of the Oxfordshire Lorry Route, via Sandy Lane

Allocation of the site is likely to have a minor effect on the local landscape character and views due to the site’s location next to the existing quarry and the partially screened nature of the site

Overall ecological impacts have the potential to be high, with the site in close proximity to a number of sensitive ecological receptors.

Site SS-19 & CR-23: Home Farm, Carswell

Site Information (as nominated in 2018) Site Location Home Farm, Carswell Grid Reference SU 328 967 Administrative Area Vale of White Horse Parish Buckland Site Nominee(s) Land and Mineral Management (agent) Proposed Development Soft sand and Crushed rock extraction. New site. Site Area 44 ha

Estimated annual 100,000 to 150,000 tpa output Estimated Reserves Estimated total yield of 1.0 mt soft (including depth/ sand Estimated total yield of 1.0 mt overburden) crushed rock Estimated working depth of up to 12m Estimated overburden of up to 2m. Proposed Restoration Agriculture with areas of ecological management/enhancement.

Access Existing purpose-built access onto Carswell Lane (A420) which connects to the A417. Estimated Unknown Traffic Movements Year of Unknown Commencement Lifetime of Unknown Operation

556 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0

Stage 1a: High Level Assessment

Criterion Comments / Justification RAG Score Compliance with Minerals • Site lies within Mineral Strategic Resource Areas for soft sand (The Corallian Ridge – Oxford Strategy – Strategic Resource to Faringdon) and, except for the a strip along the eastern boundary, for crushed rock (East / Areas (Policy M3) South East of Faringdon) in the southern part of the county (Vale of White Horse). • Site is not an extension to an existing site and appears to be currently in use as a Golf Course. • Site is adjacent to the Oxfordshire Lorry Route (A420 access). • Estimated total yield of 1.0mt of soft sand and 1.0 mt of crushed rock District Local Plan Allocation • Site is not allocated in a District Local Plan. Biodiversity and Geodiversity • Peat Bottom Wood (Ancient Woodland) overlies a small part of the southern end of the site. (Policy C7) • Site adjacent to Buckland Warren SSSI. • Site lies within 270m of a Local Geological Site (Hatford Sand Pit). • Site does not lie in close proximity to any LNR’s or NNR’s. • Site located in excess of 5km from International / European designated sites. Landscape / Visual (Policy C8) • Site not located within 3km of an AONB. Water Environment and Flooding • Site does not lie within a source protection zone. (Policy C3 and Policy C4) • Site does not lie within flood zone 2 or 3. • Site overlies a secondary aquifer. Air Quality (Policy C5) • Site not located within 1km of an AQMA. Soil Resources (Policy C6) • Approximately 35% of the site lies within an area of Grade 2 Agricultural Land and approximately 65% lies within Grade 3 Agricultural Land. Historic Environment (Policy C9) • Grade II Listed buildings at Carswell Manor (St Hugh’s School) and Barcote Manor are located approximately 700m and 560km respectively north of the workable site. Home Farm Dovecote is approximately 800m to the east. • A number of listed building are located in Littleworth approximately 1km away. • Grade II* listed Park and Garden (Buckland House) lies within 750m of the site. • Site lies within 1km of Hatford Conservation Area. • The site is located within an area of considerable archaeological interest. There is an extensive spread of cropmarks in the southern part of the site indicating enclosures and a series of linear features. They are likely to be of later prehistoric and/or Romano British origin and are probably related to a series of similar features beyond the allotment area to the south west. • Archaeological remains are likely to be undisturbed the site sensitive in archaeological terms. • There are currently no known historic landscape constraints. Transport and Access (Policy • The site access is directly to the Oxfordshire Lorry Route (A420). C10) • No AM or PM peak traffic congestion identified within proximity to site.

© Adams Hendry Consulting Ltd. 557 January 2020 Oxfordshire Mineral and Waste Sites Plan Site Options Appraisal | Version 3.0 • Site lies within close proximity to area with history of RTIs (1 serious RTI within 3km of site on A420). Public Rights of Way (Policy C11) • A public bridleway crosses through the middle of the site. Health and Amenity (Policy C5) • Site located adjacent to a residential dwelling at Carswell Home Farm and the Carswell Golf and Country Club and B&B. • Residential dwellings lie 200m to the east of the site at Ashtree Farm and approximately 300m to the west at Barcote Farm. Green Belt (Policy C12) • Site does not lie within Green Belt. Aerodrome Safeguarding (Policy • The site lies within the RAF Brize Norton buffer of airport safeguarding. M10)

Potential Cumulative Impact • Site lies within 3km of 3 existing waste sites: Shellingford Quarry, Chinham Farm and Stanford in the Vale HWRC. (minerals and waste sites) • Site lies within 3km of 3 existing minerals sites: Chinham Farm Quarry, Hatford Quarry and Shellingford Quarry. • Site lies within 3km of 3 nominated waste sites: 229 Shellingford Quarry, 230 Chinham Farm and 283 Hatford Quarry Stanford Ext. • Site lies within 3km of 7 nominated minerals sites: SS-03/CR-17, SS-07/CR-24, SS-08/CR-16, SS-12/CR-12, SS- 15/CR-11, SS-16/CR-21 and SS-18/CR-22.

Conclusion

The site is proposed as a new extraction site for crushed rock and soft sand and lies within the MSRA. The site has direct access onto the Oxfordshire Lorry Route. However, there are a number of potential constraints to the operation of this site. The site is adjacent to the Buckland Warren SSSI and overlies a small section of ancient woodland. The whole site overlies grade 2 and 3 agricultural land. There are residential dwellings and a B&B in close proximity to the site. The site appears to be currently in use as a Golf Course.

Notwithstanding the site constraints, having regard to the size of the site, its location in the MSRA and the direct access to the Oxfordshire Lorry Route, there may be some potential for mineral working and the site will be taken forward for further detailed assessment.

ASSESSMENT OUTCOME

Take forward for detailed assessment Not taken forward for detailed assessment

Stage 1b: Detailed Assessment

PLANNING HISTORY

Overview

No planning history.

ASSESSMENT

Compliance with Policy M4: Quantity and Quality of Mineral Resource SS-19: Limited borehole records available to assess quality. Two borehole records to the north and south of the site indicate the presence of a 2m layer of yellow sand. Fair

CR-23: Limited borehole records available to assess quality. Two boreholes (SU39NW30) to the north and (SU39NW38). Both of these records show limited evidence on crushed rock potential. Poor

Compliance with Policy C7: Biodiversity and Geodiversity - Ecology Officer Assessment

Irreplaceable habitats within and adjacent to the site include the ancient woodland within the site to the south and other ancient woodland immediately adjacent and several other areas within 500m. Other notable habitats within and adjacent to the site include woodlands and waterbodies.

Great Crested Newts and several bat species have been recorded in the area, both of which are protected under European law. Other protected and notable species within and adjacent to the site include several mammals, birds, amphibians, plants and invertebrates. The site is partially within the West Oxon Heights Streams, Hills, Woods & Parks Conservation Target Area (CTA).

The site is within and adjacent to several sensitive ecological receptors, notably the Buckland Warren Woods and areas of ancient woodland. Overall the potential ecological impacts of the proposals are likely to be high.

Compliance with Policy C8: Landscape - Landscape Officer Assessment

Site is not within a designated landscape or its setting. It comprises a golf course which reflects few characteristic landscape features. It is bordered by woodland to the southeast and otherwise surrounded by intensive agricultural fields. Restoration has potential to deliver landscape enhancements in the long term.

There are Public Rights of Way in the vicinity which might offer views into the site. Views from the A420 are screened by rows of conifers which are uncharacteristic elements in this landscape. The site is on sloping ground which increase visibility in views from close and distant viewpoints. Mitigation in the form of native planting and bunding is likely to assist in mitigating visual impacts.

Impacts on public views are likely to be moderate during operation. Restoration has potential to provide visual enhancements in the long term.

Overall the landscape impact is considered to be low when considered in isolation but has the potential to be much greater if other sites in the vicinity are worked at a similar time.

It is important that the cumulative impact of the various developments on the area is assessed.

Compliance with Policy C10: Transport - Highways Officer Assessment

The A420 is a strategic route known to have capacity issues in the peaks.

Existing golf club access onto the A420 appears adequate.

Conclusion

The site lies within Mineral Strategic Resource Areas for soft sand and with the exception of a strip along the eastern boundary, for crushed rock and has direct access on to the Oxfordshire Lorry Route (A420).

The landscape impact of mineral extraction is considered to be low when considered in isolation but the cumulative effects of other mineral workings in the vicinity could be much greater.

The site is within and adjacent to several sensitive ecological receptors and the impacts of mineral extraction are likely to be high.