Declaration of Compliance BS3882:2015

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Declaration of Compliance BS3882:2015 Soil source: British Sugar TOPSOIL This declaration confirms that the topsoil represented by the attached Topsoil Analysis Report conforms to the requirements of the British Standard for Topsoil (BS3882:2015). The sample was sampled and tested in accordance with the requirements of BS3882:2015 Samples are taken for analysis every 8000 tonnes (5000 m3) of product Samples are taken from all TOPSOIL products ready for despatch Landscape 20 is sampled after screening Analysis certificates are retained for a period of 5 years Laboratory analysis is undertaken at a UKAS and MCERTS accredited laboratory All laboratory methods are in accordance with BS3882:2015 All British Sugar TOPSOIL products are produced to a Quality Management System approved by Lloyd's Register Quality Assurance to ISO 9001:2008 standard Signed Andy Spetch British Sugar TOPSOIL, National TOPSOIL Manager Sugar Way, Peterborough, PE2 9AY Telephone 0870 2402314

Mr Andy Spetch Oundle Road Peterborough PE2 9QU Dear Mr Spetch Topsoil Analysis Report: Bury St Edmunds Bury L20 20 th October 2017 Our Ref: TOHA/17/7338/SS Your Ref: 60035574 We have completed the analysis of the LANDSCAPE 20 TOPSOIL sample recently submitted, referenced Bu-L20-8KT-Oct17 and have pleasure reporting our findings. The purpose of the analysis was to determine the suitability of the LANDSCAPE 20 TOPSOIL sample for general landscape purposes. In addition, this sample has been assessed to determine its compliance with the requirements of the British Standard for Topsoil (BS3882:2015 - Specification for topsoil Table 1, Multipurpose Topsoil). This report presents the results of analysis for the sample submitted to our office, and it should be considered indicative of the topsoil source. The report and results should therefore not be used by third parties as a means of verification or validation testing or waste designation purposes, especially after the topsoil has left the British Sugar factory. SAMPLE EXAMINATION The sample was described as a dark greyish brown (Munsell Colour 10YR 4/2), moist, slightly plastic, moderately calcareous SANDY CLAY LOAM with a weakly developed, fine to medium granular structure*. The sample was virtually stone-free and no unusual odours, deleterious materials, roots or rhizomes of pernicious weeds were observed. *This appraisal of soil structure was made from examination of a disturbed sample. Structure is a key soil characteristic that may only be accurately assessed by examination in an in-situ state. T i m O H a r e A s s o c i a t e s L L P H o w b e r y P a r k W a l l i n g f o r d O x f o r d s h i r e O X 1 0 8 B A T : 0 1 4 9 1 8 2 2 6 5 3 E : i n f o @ t o h a. c o. u k w w w. t o h a. c o. u k Registered in England No. OC324049 Registered Office: The Innovation Centre, Howbery Park, Wallingford, Oxfordshire OX10 8BA

LANDSCAPE 20 TOPSOIL Analysis Bury St Edmunds Bu-L20-8KT-Oct17 Tim O Hare Associates ANALYTICAL SCHEDULE The sample was submitted to a UKAS and MCERTS accredited laboratory for a range of physical and chemical tests to confirm the composition and fertility of the soil, and the concentration of selected potential contaminants. The following parameters were determined: particle size analysis and stone content; ph and electrical conductivity values; exchangeable sodium percentage; major plant nutrients (N, P, K, Mg); organic matter content; C:N ratio; heavy metals (As, B, Ba, Be, Cd, Cr, Cu, Pb, Hg, Ni, Se, V, Zn); total cyanide and total (mono) phenols; aromatic and aliphatic TPH (C5-C35 banding); speciated PAHs (US EPA16 suite); benzene, toluene, ethylbenzene, xylene; asbestos screen. The results are presented on the attached Certificate of Analysis and an interpretation of the results is given below. The interpretation considers the use of the LANDSCAPE 20 TOPSOIL for general landscape purposes and its compliance/non-compliance with our general landscape specification. RESULTS OF ANALYSIS Particle Size Analysis and Stone Content The sample fell into the sandy clay loam texture class, which is usually considered suitable for general landscape applications provided the soil s physical condition is satisfactory. Such soils usually have good water and nutrient retention capacities, but they are also prone to structural degradation and compaction during handling, and especially when plastic in consistency. Any damage to the structural condition of this soil is likely to reduce its drainage and aeration properties. The sample was virtually stone-free and as such, stones should not restrict the use of the soil for general landscape purposes. ph and Electrical Conductivity Values The sample was alkaline in reaction (ph 7.6). This ph value would be considered suitable for general landscape purposes providing species with a wide ph tolerance or those known to prefer alkaline soils are selected for planting, turfing and seeding. The electrical conductivity (salinity) value (water extract) was moderate, which indicates that soluble salts should not be present at levels that would be harmful to plants. The electrical conductivity value by CaSO4 extract (BS3882 requirement) fell below the maximum specified value (3300 μs/cm) given in BS3882:2015 Table 1. Organic Matter and Fertility Status The sample was adequately supplied with organic matter and all major plant nutrients. The C:N ratio of the sample was acceptable for general landscape purposes. Potential Contaminants With reference to BS3882:2015 - Table 1: Notes 3 and 4, there is a recommendation to confirm levels of potential contaminants in relation to the topsoil s proposed end use. This includes human health, environmental protection and metals considered toxic to plants. In the absence of site-specific criteria, the concentrations that affect human health have been assessed for residential with home grown produce end- TOHA/17/7338/SS/Oct Page 2

LANDSCAPE 20 TOPSOIL Analysis Bury St Edmunds Bu-L20-8KT-Oct17 Tim O Hare Associates use against the Suitable For Use Levels (S4ULs) presented in the LQM/CIEH S4ULs for Human Health Risk Assessment (2015) and the DEFRA SP1010: Development of Category 4 Screening Levels for Assessment of Land Affected by Contamination Policy Companion Document (2014). The concentration of barium has been compared with the residential land use given in the document EIC/AGS/CL:AIRE Soil Generic Assessment Criteria for Human Health Risk Assessment (2010). Of the potential contaminants determined, none was found at levels that exceeded their guideline values. Phytotoxic Contaminants Of the phytotoxic (toxic to plants) contaminants determined (copper, nickel, zinc), none was found at levels that exceeded the maximum permissible levels specified in BS3882:2015 Table 1. CONCLUSION The purpose of the analysis was to determine the suitability of the LANDSCAPE 20 TOPSOIL sample for general landscape purposes. From the soil examination and subsequent laboratory analysis, the sample was described as an alkaline, nonsaline, moderately calcareous sandy clay loam with a weakly developed structure and low stone content. The sample was adequately supplied with organic matter and all major plant nutrients. Of the potential contaminants determined, none was found at levels that exceeded their guideline values. Based on our findings, the topsoil represented by this sample would be considered suitable for general landscape purposes (trees, shrubs and amenity grass), provided species with a wide ph tolerance or those known to prefer alkaline soils are selected for planting and the physical condition of the soil is satisfactory. The topsoil was also fully compliant with the requirements of the British Standard for Topsoil (BS3882:2015 Specification for Topsoil - Table 1, Multipurpose Topsoil). RECOMMENDATIONS Soil Handling Recommendations It is important to maintain the physical condition of the soil and avoid structural damage during all phases of soil handling (e.g. stockpiling, respreading, cultivating, planting). As a consequence, soil handling operations should be carried out when soil is reasonably dry and non-plastic (friable) in consistency. It is important to ensure that the soil is not unnecessarily compacted by trampling or trafficking by site machinery, and soil handling should be stopped during and after heavy rainfall and not continued until the soil is friable in consistency. If the soil is structurally damaged and compacted at any stage during the course of soiling or landscaping works, it should be cultivated appropriately to relieve the compaction and to restore the soil s structure prior to any planting, turfing or seeding. Further details on soil handling are provided in Annex A of BS3882:2015. Further guidance on the management, preparation and handling of soils is provided in the DEFRA publication Construction code of practice for the sustainable use of soils on construction sites, 2009. TOHA/17/7338/SS/Oct Page 3

LANDSCAPE 20 TOPSOIL Analysis Bury St Edmunds Bu-L20-8KT-Oct17 Tim O Hare Associates We hope this report meets with your approval and provides the necessary information. Please do not hesitate to contact the undersigned if we can be of further assistance. Yours sincerely Ruth Flower BSc Graduate Soil Scientist For & on behalf of Tim O Hare Associates LLP Laura Hathaway-Jenkins BSc MSc EngD MISoilSci Senior Associate TOHA/17/7338/SS/Oct Page 4

Client: Client Ref: Bury St Edmunds Job: Topsoil Analysis Date: 20/10/2017 Job Ref No: TOHA/17/7338/SS Sample Reference Bu-L20-8KT-Oct17 Clay (<0.002mm) % U 23 Silt (0.002-0.063mm) % U 24 Sand (0.063-2.0mm) % U 53 Texture Class (UK Classification) -- U SCL -- Stones (2-20mm) % DW G 1 Stones (20-50mm) % DW G 1 Stones (>50mm) % DW G 0 ph Value (1:2.5 water extract) units G 7.6 Electrical Conductivity (1:2.5 water extract) us/cm U 1370 Electrical Conductivity (1:2 CaSO 4 extract) us/cm U 2780 Exchangeable Sodium Percentage % U 5.0 Moisture Content % U 17 -- Organic Matter (LOI) % U 6.0 Total Nitrogen (Dumas) % U 0.42 C : N Ratio :1 U 8 Extractable Phosphorus mg/l U 76 Extractable Potassium mg/l U 902 Extractable Magnesium mg/l U 103 Total Arsenic (As) mg/kg M 11 Total Barium (Ba) mg/kg M 56 Total Beryllium (Be) mg/kg M 0.71 Total Cadmium (Cd) mg/kg M 0.4 Total Chromium (Cr) mg/kg M 25 Hexavalent Chromium (Cr VI) mg/kg M < 4.0 Total Copper (Cu) mg/kg M 29 Total Lead (Pb) mg/kg M 25 Total Mercury (Hg) mg/kg M < 0.3 Total Nickel (Ni) mg/kg M 17 Total Selenium (Se) mg/kg M < 1.0 Total Vanadium (V) mg/kg M 37 Total Zinc (Zn) mg/kg M 72 Water Soluble Boron (B) mg/kg M 2.7 Total Cyanide (CN) mg/kg M < 1 Total (mono) Phenols mg/kg M < 1.0 Naphthalene mg/kg M < 0.05 Acenaphthylene mg/kg M < 0.05 Acenaphthene mg/kg M < 0.05 Fluorene mg/kg M < 0.05 Phenanthrene mg/kg M 0.15 Anthracene mg/kg M < 0.05 Fluoranthene mg/kg M 0.27 Pyrene mg/kg M 0.22 Benzo(a)anthracene mg/kg M 0.16 Chrysene mg/kg M 0.15 Benzo(b)fluoranthene mg/kg M 0.2 Benzo(k)fluoranthene mg/kg M 0.13 Benzo(a)pyrene mg/kg M 0.16 Indeno(1,2,3-cd)pyrene mg/kg M < 0.05 Dibenzo(a,h)anthracene mg/kg M < 0.05 Benzo(g,h,i)perylene mg/kg M < 0.05 Total PAHs (sum USEPA16) mg/kg M 1.44 Aliphatic TPH (C5-C6) Aliphatic TPH (C6-C8) Aliphatic TPH (C8-C10) Aliphatic TPH (C10-C12) mg/kg M < 1.0 Aliphatic TPH (C12-C16) mg/kg M < 2.0 Aliphatic TPH (C16-C21) mg/kg M < 8.0 Aliphatic TPH (C21-C35) mg/kg M 27 Aliphatic TPH (C5-C35) mg/kg M 34 Aromatic TPH (C5-C7) Aromatic TPH (C7-C8) Aromatic TPH (C8-C10) Aromatic TPH (C10-C12) mg/kg M 1.5 Aromatic TPH (C12-C16) mg/kg M < 2.0 Aromatic TPH (C16-C21) mg/kg M < 10 Aromatic TPH (C21-C35) mg/kg M 35 Aromatic TPH (C5-C35) mg/kg M 43 Benzene Toluene Ethylbenzene o-xylene m & p-xylene Asbestos ND/D I Not-detected Visual Examination The sample was described as a dark greyish brown (Munsell Colour 10YR 4/2), moist, slightly plastic, moderately calcareous SANDY CLAY LOAM with a weakly developed, fine to medium granular structure. The sample was virtually stone-free and no unusual odours, deleterious materials, roots or rhizomes of pernicious weeds were observed. X SCL M I U G Meets General Landscape Specification Fails General Landscape Specification SANDY CLAY LOAM Texture Class MCERTS accredited method (& UKAS accredited method) ISO 17025 accredited method UKAS accredited method GLP accredited method This report presents the results of analysis for the sample submitted to our office, and it should be considered indicative of the topsoil source. The report and results should therefore not be used by third parties as a means of verification or validation testing. Results of analysis should be read in conjunction with the report they were issued with Ruth Flower BSc Graduate Soil Scientist The contents of this certificate shall not be reproduced without the express written permission of Tim O'Hare Associates LLP. Tim O'Hare Associates LLP Howbery Park Wallingford Oxfordshire OX10 8BA www.toha.co.uk