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EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:392: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:393: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:394: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:395: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:20:been consistently identified in offsite monitoring wells SBA_AUK_BH110, and in SBA_AUK_BH105.

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:27:The Arcadis 2021c report, identified NAPL present adjacent to the SBCO by-product plant (SBA_AUK_BH110

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:28: Creep observed in wells SBC_AUK_BH109S and SBC_AUK_BH110S

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:683:SBC_AUK_BH110S

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:684:SBC_AUK_BH110S

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:685:SBC_AUK_BH110S

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:687:SBC_AUK_BH110S

R-2021-0855-CD-MGE04603 Contaminated Land.pdf:2:Contamination from the Groundwater Source in the vicinity of SBA_AUK_BH110 is

R-2021-0855-CD-MGE04603 Contaminated Land.pdf:2:concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110

R-2021-0855-CD-MGE04603 Contaminated Land.pdf:2:Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:5: Groundwater source in the vicinity of SBC_AUK_BH110 considered to

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:7: undertaken in this DQRA, the Groundwater Source in the area of SBA_AUK_BH110

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:18:Dense Non-Aqueous Phase Liquid (DNAPL) was measured in SBA_AUK_BH110 in two of the three

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:18: Groundwater Source in the vicinity of SBA_AUK_BH110 considered to represent contamination

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:20:contaminant concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110 and the

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:21:A NAPL source within the groundwater has been recorded in SBA_AUK_BH110 towards the southern

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:21:plume located north towards the River Tees from the SBA_AUK_BH110 area is present. The NAPL was found

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:21:The groundwater source identified in the vicinity of SBA_AUK_BH110 is considered to form a potentially

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:deposits in SBA_AUK_BH110 at the southern boundary of the site. The NAPL thickness was measured on

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:SBCO area investigation. However, SBA_AUK_BH110 in SBA was the only well from which a measurable

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:include SBA_AUK_BH105 and SBA_AUK_BH110 in the south of SBA where odours, sheen and tar were

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:Higher sum TPH concentrations were measured in SBA_AUK_BH110, but these were saturated so are best

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:The highest concentration of sum TPH was measured in SBA_AUK_BH110, located in the south of SBA and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:27:BTEX. The highest concentrations were measure in SBA_AUK_BH110, located in the south of SBA, and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:27:concentration of 2,100µg/l was measured in SBC_AUK_BH107, to the south of SBA_AUK_BH110 and in the

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:27:well locations respectively. Highest concentrations were again measured in SBA_AUK_BH110, with toluene

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:27:concentrations were measured in SBA_AUK_BH110, with sum PAH ranging from 6,000ug/l to 11,000ug/l

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:28:1,400µg/l measured in SBC_AUK_BH107 and a maximum of 690µg/l measured in SBA_AUK_BH110. This

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29:highest measured concentration in downgradient monitoring well SBC_AUK_BH110. However, the highest

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29:were measured in SBA_AUK_BH110 adjacent to the southern boundary of SBA, which separates SBA from

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29:BH110 also had a measured thickness of DNAPL on two of the three groundwater monitoring visits

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29:SBA_AUK_ BH110 associated with the Groundwater Source, where contaminants (including hydrocarbons,

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29: Groundwater Source in the vicinity of SBA_AUK_BH110 considered to represent impacts

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: 8,900 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: Aromatic >EC12- 1,600 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: Benzene 2,400 1 47,000 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: 11,000 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: 260 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: Anthracene 30 1 52 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: 100 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:36: Monohydric Phenols 2,310 1 16,000 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:37: 690 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:37: 62,000 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:37: 31,000 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:38: Hexavalent Chromium 180 1 280 (SBA_AUK_BH110)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:41: SBA_AUK_BH110

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:41:SBA_AUK_BH105, SBA_AUK_BH110, SBC_AUK_BH106, SBC_AUK_BH107, SBC_AUK_BH112 and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:41:SBC_AUK_BH114. SBA_AUK_BH105 and SBA_AUK_BH110 were included in the modelled groundwater

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:41:SBA_AUK_BH110 in relatively close proximity (approximately 70m). SBC_AUK_BH106 is to the east of

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:43:this DQRA, the Groundwater Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2021-0855-CD-Officer report.pdf:3:Contamination from the Groundwater Source in the vicinity of SBA_AUK_BH110 is

R-2021-0855-CD-Officer report.pdf:3:concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110

R-2021-0855-CD-Officer report.pdf:3:Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1265: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1266: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1267: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1268: Sample ID MS\BH108 MS\BH110 MS\BH112 MS\BH114

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000008_App_D-2.pdf:1: PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part9.pdf:34: PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:13: BH110 on 3rd July.

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:16: BH110 - screening Mercia Mudstone

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:17:Both BH108D and BH110 screen the Mercia Mudstone and as such will be considered together. A total of 12

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:17:concentrations of NaCl in groundwater sampled from the remaining two samples (BH109 and BH110) were

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:18:measured in groundwater samples with the exception of groundwater in BH109 and BH110 during monitoring

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:18:in June and July 2020. Both BH109 and BH110 screen bedrock in the west of the site and groundwater

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:21:monitoring visits was measured in BH110 (screening the Mercia Mudstone) in June 2020 at a concentration

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:21:in the groundwater were an order of magnitude lower than those observed in monitoring well BH110.

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:46:Sample Identity PRAIRIE_AUK_BH110_GW_190620 PRAIRIE_AUK_BH103_GW_050520 WS7

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000007_App_D-1.pdf:1: E = 454250 PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:107: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:108: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:109: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:164: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:165: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:168: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:169: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:174: Sample ID BH108 BH109 BH110 _SW4

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part11.pdf:175: Sample ID BH108 BH109 BH110 _SW4

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:8: Prairie_AUK_BH110 Mercia Mudstone 3.8 3.96 3.93 3.84 - 4.00

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9: BH110 - screening Mercia Mudstone

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:three slug insertions) were completed in BH108D and BH110 and four tests (two slug extractions and two slug

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The hydraulic

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:11: Prairie_AUK_BH110 Mercia Mudstone 134 1068.3 1235.9

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:  Prairie_AUK_BH110 (2nd and 3rd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:Concentrations of total cyanide in Prairie_AUK_BH101S/D and Prairie_AUK_BH110 were generally higher

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:than elsewhere. The highest concentration of free cyanide was measured in Prairie_AUK_BH110.

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:  Prairie_AUK_BH110 (2nd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: Prairie_AUK_BH110 Mercia Mudstone

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: Cadmium μg/l 9/36 EQS 0.2 PRAIRIE_AUK_BH110 (2nd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: PRAIRIE_AUK_BH110 (2nd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: PRAIRIE_AUK_BH110 (1st and 2nd visits)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: PRAIRIE_AUK_BH110(1st and 3rd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: Total Cyanide μg/l PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:20: PRAIRIE_AUK_BH110 (1st and 3rd visits)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:38:(PRAIRIE_AUK_BH110).

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:39:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:41:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:57:UK_BH110 slotted standpipe

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:84: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:85: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:86: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:87: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: Figure PRAIRIE_AUK_BH110.1

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: Figure PRAIRIE_AUK_BH110.2

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:91:PRAIRIE_AUK_TP149 Machine excavated 3.00 Continued as PRAIRIE_AUK_BH110.

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 4.00 3.80

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 3.84 3.96

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 3.87 3.93

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Fair 14 7.80 4.00 3.80 -0.8 -2.25 1028 0.5 0.5 10.0 10.0 0.1 0.1 20.4 20.4 1.0 3.0

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Overcast 15 7.80 3.84 3.96 0.1 -0.07 1016 0.1 0.1 2.0 2.0 0.2 0.2 11.9 11.9 <0.1 32.0

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Overcast 15 7.80 3.87 3.93 0.1 -0.21 1001 0.1 0.1 2.0 2.0 0.4 0.4 5.5 5.5 <1.0 13

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:555: BH110 10:35:00 7.60 12.47 4045.00 169.00 8.49 3.45

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:908: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:909: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:910: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:911: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1170: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1171: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1172: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1173: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1184: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1185: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1260:1668118 PRAIRIE_AUK_BH110_SO_0300 1 SOIL NAD none Lee Kerridge

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1298:1668118 PRAIRIE_AUK_BH110_SO_0 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1303:1671904 PRAIRIE_AUK_BH110_GW_ 06/05/20 GB 1L x2, GV, PB 1L

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1323: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1324: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1325: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1326:1694900 PRAIRIE_AUK_BH110_ 02/07/20 GB 1L, GV, PB 1L, PU

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1337:1688256 PRAIRIE_AUK_BH110_ 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Glaciolacustrine Deposits), BH108D and BH110 (both screening Mercia Mudstone) on 3rd July 2020. An

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Slug tests were performed on monitoring wells BH101D, BH103, BH108D and BH110, to provide an estimate

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Rice’s method for a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1419: Well ID BH110 - T1 BH110 - T2 BH110 - T3 BH110 - T4 BH110 - T5 BH110 - T6 BH108D- T1 BH108D- T2 BH108D- T3 BH108D- T4 BH108D- T5 BH108D- T6 BH101D - T1 BH101D - T2 BH101D - T3 BH101D - T4

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:7: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:8: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:9: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:24:1668118 PRAIRIE_AUK_BH110 1 3.00 PRAIRIE_AUK_B SOIL NAD none Lee Kerridge

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:38:1668118 PRAIRIE_AUK_BH110 3.00 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:41:1671904 PRAIRIE_AUK_BH110 4.00- 06/05/20 GB 1L x2, GV, PB 1L

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:42:1688256 PRAIRIE_AUK_BH110 3.84- 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:43:1694900 PRAIRIE_AUK_BH110 3.87- 02/07/20 GB 1L, GV, PB 1L, PU

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:8:(PRAIRIE_AUK_BH110).

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:9:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:11:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:23: PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:24:RIE_AUK_BH110 PRAIRIE_AUK_TP141 Teesside Management Office, Trunk Road,

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:25: PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:27:UK_BH110 slotted standpipe

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:54: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:55: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:56: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:57: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:58: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:58: Figure PRAIRIE_AUK_BH110.1

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:58: Figure PRAIRIE_AUK_BH110.2

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part1.pdf:61: Continued as PRAIRIE_AUK_BH110. Advanced to required

R-2021-0100-CD-Phase II ESA.pdf:21: Prairie_AUK_BH110 Mercia Mudstone 4.00 3.798

R-2021-0100-CD-Phase II ESA.pdf:49: Prairie_AUK_BH110 Mercia Mudstone

R-2021-0100-CD-Phase II ESA.pdf:50: PRAIRIE_AUK_BH110 180

R-2021-0100-CD-Phase II ESA.pdf:488: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-Phase II ESA.pdf:489: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-Phase II ESA.pdf:490: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-Phase II ESA.pdf:491: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-Phase II ESA.pdf:492: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0100-CD-Phase II ESA.pdf:492: Figure PRAIRIE_AUK_BH110.1

R-2021-0100-CD-Phase II ESA.pdf:492: Figure PRAIRIE_AUK_BH110.2

R-2021-0100-CD-Phase II ESA.pdf:664: BH108D_GW_0 BH110_GW_06

R-2021-0100-CD-Phase II ESA.pdf:665: BH108D_GW_0 BH110_GW_06

R-2021-0100-CD-Phase II ESA.pdf:666: BH108D_GW_0 BH110_GW_06

R-2021-0100-CD-Phase II ESA.pdf:673: BH108S_GW_0 BH108D_GW_0 BH110_GW_06

R-2021-0100-CD-Phase II ESA.pdf:674: BH108S_GW_0 BH108D_GW_0 BH110_GW_06

R-2021-0100-CD-Phase II ESA.pdf:701:1668118 PRAIRIE_AUK_BH110_SO_0300 1 SOIL NAD none Lee Kerridge

R-2021-0100-CD-Phase II ESA.pdf:723:1668118 PRAIRIE_AUK_BH110_SO_0 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2021-0100-CD-Phase II ESA.pdf:726:1671904 PRAIRIE_AUK_BH110_GW_ 06/05/20 GB 1L x2, GV, PB 1L Aliphatics/Aromatics (4 days),

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:22: PRAIRIE_AUK_BH110 10.30 -2.50 Encountered within Glaciolacustrine Deposits

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:41:PRAIRIE_AUK_BH110 at the northern end of the site decreasing to 4.6m recorded in PRAIRIE_AUK_BH109 at

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:44:PRAIRIE_AUK_BH110 underlying the superficial deposits. The material was typically described as extremely

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:44:(PRAIRIE_AUK_BH110) to 1.46m AOD at the centre of the site, and was expected to decrease southwards as

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:52:PRAIRIE_AUK_BH107 20m east of the eastern culvert, and PRAIRIE_AUK_BH110 110m north of the northern

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:52:Glaciolacustrine Deposits encountered between 5.0m bgl and 7.5m bgl within PRAIRIE_AUK_BH110 which

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Glaciolacustrine Deposits), BH108D and BH110 (both screening Mercia Mudstone) on 3rd July 2020. An

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Slug tests were performed on monitoring wells BH101D, BH103, BH108D and BH110, to provide an estimate

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Rice’s method for a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part4.PDF:23: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:82: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:83: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:84: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:139: Sample ID BH110 SW1 SW2 BH101 BH101

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:140: Sample ID BH110 SW1 SW2 BH101 BH101

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:143: Sample ID BH107 BH108 BH108 BH109 BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:144: Sample ID BH107 BH108 BH108 BH109 BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:149: Sample ID BH108 BH109 BH110 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:150: Sample ID BH108 BH109 BH110 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:157: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:158: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:159: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:174:1668118 PRAIRIE_AUK_BH110 1 3.00 PRAIRIE_AUK_B SOIL NAD none Lee Kerridge

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:12:1668118 PRAIRIE_AUK_BH110 3.00 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:15:1671904 PRAIRIE_AUK_BH110 4.00- 06/05/20 GB 1L x2, GV, PB 1L

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:16:1688256 PRAIRIE_AUK_BH110 3.84- 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:17:1694900 PRAIRIE_AUK_BH110 3.87- 02/07/20 GB 1L, GV, PB 1L, PU

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:51: Sample ID BH110 SW1 SW2 BH101 BH101

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:52: Sample ID BH110 SW1 SW2 BH101 BH101

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:55: Sample ID BH107 BH108 BH108 BH109 BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:56: Sample ID BH107 BH108 BH108 BH109 BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:61: Sample ID BH108 BH109 BH110 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:62: Sample ID BH108 BH109 BH110 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:69: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:70: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:71: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:86:1668118 PRAIRIE_AUK_BH110 1 3.00 PRAIRIE_AUK_B SOIL NAD none Lee Kerridge

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:100:1668118 PRAIRIE_AUK_BH110 3.00 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:103:1671904 PRAIRIE_AUK_BH110 4.00- 06/05/20 GB 1L x2, GV, PB 1L

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:104:1688256 PRAIRIE_AUK_BH110 3.84- 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:105:1694900 PRAIRIE_AUK_BH110 3.87- 02/07/20 GB 1L, GV, PB 1L, PU

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:8: Prairie_AUK_BH110 Mercia Mudstone 3.8 3.96 3.93 3.84 - 4.00

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:• BH110 - screening Mercia Mudstone

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:three slug insertions) were completed in BH108D and BH110 and four tests (two slug extractions and two slug

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The hydraulic

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:11: Prairie_AUK_BH110 Mercia Mudstone 134 1068.3 1235.9

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13: • Prairie_AUK_BH110 (2nd and 3rd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:Concentrations of total cyanide in Prairie_AUK_BH101S/D and Prairie_AUK_BH110 were generally higher

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:than elsewhere. The highest concentration of free cyanide was measured in Prairie_AUK_BH110.

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13: • Prairie_AUK_BH110 (2nd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: Prairie_AUK_BH110 Mercia Mudstone

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: Cadmium μg/l 9/36 EQS 0.2 PRAIRIE_AUK_BH110 (2nd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: PRAIRIE_AUK_BH110 (2nd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: PRAIRIE_AUK_BH110 (1st and 2nd visits)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: PRAIRIE_AUK_BH110(1st and 3rd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: Total Cyanide μg/l PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:20: PRAIRIE_AUK_BH110 (1st and 3rd visits)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:38:(PRAIRIE_AUK_BH110).

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:39:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:41:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:53: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:54:RIE_AUK_BH110 PRAIRIE_AUK_TP141 Teesside Management Office, Trunk Road,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:55: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:57:UK_BH110 slotted standpipe

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:84: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:85: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:86: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:87: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: Figure PRAIRIE_AUK_BH110.1

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: Figure PRAIRIE_AUK_BH110.2

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:91: Continued as PRAIRIE_AUK_BH110. Advanced to required

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:290: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:291: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:292: Sample ID TP187 BH110 TP102 TP102 TP103

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:21: Prairie_AUK_BH110 Mercia Mudstone 4.00 3.798

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:49: Prairie_AUK_BH110 Mercia Mudstone

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:50: PRAIRIE_AUK_BH110 180

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part3.PDF:120: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:15:(PRAIRIE_AUK_BH110).

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:16:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:18:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:30: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:31:RIE_AUK_BH110 PRAIRIE_AUK_TP141 Teesside Management Office, Trunk Road,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:32: PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:34:UK_BH110 slotted standpipe

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:61: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:62: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:63: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:64: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: Figure PRAIRIE_AUK_BH110.1

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: Figure PRAIRIE_AUK_BH110.2

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:68: Continued as PRAIRIE_AUK_BH110. Advanced to required

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:45: • Groundwater source in the vicinity of SBC_AUK_BH110 - considered to represent

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:45: • Groundwater source in the vicinity of SBC_AUK_BH110 - considered to represent

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:13: BH110 on 3rd July.

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:16: BH110 - screening Mercia Mudstone

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:17:Both BH108D and BH110 screen the Mercia Mudstone and as such will be considered together. A total of 12

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:17:concentrations of NaCl in groundwater sampled from the remaining two samples (BH109 and BH110) were

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:18:measured in groundwater samples with the exception of groundwater in BH109 and BH110 during monitoring

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:18:in June and July 2020. Both BH109 and BH110 screen bedrock in the west of the site and groundwater

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:21:monitoring visits was measured in BH110 (screening the Mercia Mudstone) in June 2020 at a concentration

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:21:in the groundwater were an order of magnitude lower than those observed in monitoring well BH110.

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:46:Sample Identity PRAIRIE_AUK_BH110_GW_190620 PRAIRIE_AUK_BH103_GW_050520 WS7

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:8: Prairie_AUK_BH110 Mercia Mudstone 3.8 3.96 3.93 3.84 - 4.00

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9: BH110 - screening Mercia Mudstone

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:three slug insertions) were completed in BH108D and BH110 and four tests (two slug extractions and two slug

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The hydraulic

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:9:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:11: Prairie_AUK_BH110 Mercia Mudstone 134 1068.3 1235.9

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:  Prairie_AUK_BH110 (2nd and 3rd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:Concentrations of total cyanide in Prairie_AUK_BH101S/D and Prairie_AUK_BH110 were generally higher

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:than elsewhere. The highest concentration of free cyanide was measured in Prairie_AUK_BH110.

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:  Prairie_AUK_BH110 (2nd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: Prairie_AUK_BH110 Mercia Mudstone

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: Cadmium μg/l 9/36 EQS 0.2 PRAIRIE_AUK_BH110 (2nd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: PRAIRIE_AUK_BH110 (2nd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:18: PRAIRIE_AUK_BH110 (1st and 2nd visits)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: PRAIRIE_AUK_BH110(1st and 3rd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: Total Cyanide μg/l PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:19: PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:20: PRAIRIE_AUK_BH110 (1st and 3rd visits)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:38:(PRAIRIE_AUK_BH110).

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:39:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:41:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:57:UK_BH110 slotted standpipe

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:84: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:85: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:86: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:87: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: Figure PRAIRIE_AUK_BH110.1

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:88: Figure PRAIRIE_AUK_BH110.2

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:91:PRAIRIE_AUK_TP149 Machine excavated 3.00 Continued as PRAIRIE_AUK_BH110.

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 4.00 3.80

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 3.84 3.96

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:499:PRAIRIE_AUK_BH110 7.80 3.87 3.93

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Fair 14 7.80 4.00 3.80 -0.8 -2.25 1028 0.5 0.5 10.0 10.0 0.1 0.1 20.4 20.4 1.0 3.0

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Overcast 15 7.80 3.84 3.96 0.1 -0.07 1016 0.1 0.1 2.0 2.0 0.2 0.2 11.9 11.9 <0.1 32.0

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:503:PRAIRIE_AUK_BH110 Overcast 15 7.80 3.87 3.93 0.1 -0.21 1001 0.1 0.1 2.0 2.0 0.4 0.4 5.5 5.5 <1.0 13

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:555: BH110 10:35:00 7.60 12.47 4045.00 169.00 8.49 3.45

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:908: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:909: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:910: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:911: Sample ID PRAIRIE_AUK_BH110_SO_0300

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1170: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1171: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1172: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1173: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1184: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1185: PRAIRIE_AUK_BH108D PRAIRIE_AUK_BH110_

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1260:1668118 PRAIRIE_AUK_BH110_SO_0300 1 SOIL NAD none Lee Kerridge

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1298:1668118 PRAIRIE_AUK_BH110_SO_0 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1303:1671904 PRAIRIE_AUK_BH110_GW_ 06/05/20 GB 1L x2, GV, PB 1L

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1323: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1324: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1325: PRAIRIE_AUK_BH109_GW PRAIRIE_AUK_BH110_GW

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1326:1694900 PRAIRIE_AUK_BH110_ 02/07/20 GB 1L, GV, PB 1L, PU

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1337:1688256 PRAIRIE_AUK_BH110_ 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Glaciolacustrine Deposits), BH108D and BH110 (both screening Mercia Mudstone) on 3rd July 2020. An

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Slug tests were performed on monitoring wells BH101D, BH103, BH108D and BH110, to provide an estimate

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:Rice’s method for a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1415:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1419: Well ID BH110 - T1 BH110 - T2 BH110 - T3 BH110 - T4 BH110 - T5 BH110 - T6 BH108D- T1 BH108D- T2 BH108D- T3 BH108D- T4 BH108D- T5 BH108D- T6 BH101D - T1 BH101D - T2 BH101D - T3 BH101D - T4

R-2020-0318-FFM-Phase II ESA.PDF:21: Prairie_AUK_BH110 Mercia Mudstone 4.00 3.798

R-2020-0318-FFM-Phase II ESA.PDF:49: Prairie_AUK_BH110 Mercia Mudstone

R-2020-0318-FFM-Phase II ESA.PDF:50: PRAIRIE_AUK_BH110 180

R-2020-0318-FFM-Phase II ESA.PDF:488: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-Phase II ESA.PDF:489: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-Phase II ESA.PDF:490: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-Phase II ESA.PDF:491: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-Phase II ESA.PDF:492: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2020-0318-FFM-Phase II ESA.PDF:492: Figure PRAIRIE_AUK_BH110.1

R-2020-0318-FFM-Phase II ESA.PDF:492: Figure PRAIRIE_AUK_BH110.2

R-2020-0318-FFM-Phase II ESA.PDF:664: BH108D_GW_0 BH110_GW_06

R-2020-0318-FFM-Phase II ESA.PDF:665: BH108D_GW_0 BH110_GW_06

R-2020-0318-FFM-Phase II ESA.PDF:666: BH108D_GW_0 BH110_GW_06

R-2020-0318-FFM-Phase II ESA.PDF:673: BH108S_GW_0 BH108D_GW_0 BH110_GW_06

R-2020-0318-FFM-Phase II ESA.PDF:674: BH108S_GW_0 BH108D_GW_0 BH110_GW_06

R-2020-0318-FFM-Phase II ESA.PDF:701:1668118 PRAIRIE_AUK_BH110_SO_0300 1 SOIL NAD none Lee Kerridge

R-2020-0318-FFM-Phase II ESA.PDF:723:1668118 PRAIRIE_AUK_BH110_SO_0 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2020-0318-FFM-Phase II ESA.PDF:726:1671904 PRAIRIE_AUK_BH110_GW_ 06/05/20 GB 1L x2, GV, PB 1L Aliphatics/Aromatics (4 days),

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Dibenzo(a,h)anthracene mg/kg S4UL 3.5 SBA_AUK_BH110_SO_0720 47

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Naphthalene mg/kg Wood 1,900 SBA_AUK_BH110_SO_0720 15,000

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Benzo(a)anthracene mg/kg S4UL 170 SBA_AUK_BH110_SO_0720 770

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Chrysene mg/kg S4UL 350 SBA_AUK_BH110_SO_0720 590

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Benzo(b)fluoranthene mg/kg S4UL 44 SBA_AUK_BH110_SO_0720 490

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Benzo(a)pyrene mg/kg Wood 77 SBA_AUK_BH110_SO_0720 460

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Benzene mg/kg S4UL 27 SBA_AUK_BH110_SO_0720 580

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: 2-Methylnaphthalene mg/kg USEPA 1,000 SBA_AUK_BH110_SO_0720 3,700

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16: Dibenzofuran mg/kg USEPA 1,000 SBA_AUK_BH110_SO_0720 2,900

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16:however the exceedances for these contaminants in SBA_AUK_BH110_SO_0720 and 2AB01 is within

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:16:groundwater from SBA_AUK_BH110 were below the Human Health GAC and as such do not pose a

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:17:SBA_AUK_BH110_SO_0720 and 2AB01 are considered to represent the same groundwater source.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:17: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:5:  Groundwater source in the vicinity of SBC_AUK_BH110 – considered to

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:7: undertaken in this DQRA, the Groundwater Source in the area of SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:18:Dense Non-Aqueous Phase Liquid (DNAPL) was measured in SBA_AUK_BH110 in two of the three

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:18:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent contamination

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:20:contaminant concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110 and the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:21:A NAPL source within the groundwater has been recorded in SBA_AUK_BH110 towards the southern

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:21:plume located north towards the River Tees from the SBA_AUK_BH110 area is present. The NAPL was found

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:21:The groundwater source identified in the vicinity of SBA_AUK_BH110 is considered to form a potentially

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:deposits in SBA_AUK_BH110 at the southern boundary of the site. The NAPL thickness was measured on

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:SBCO area investigation. However, SBA_AUK_BH110 in SBA was the only well from which a measurable

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:include SBA_AUK_BH105 and SBA_AUK_BH110 in the south of SBA where odours, sheen and tar were

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:Higher sum TPH concentrations were measured in SBA_AUK_BH110, but these were saturated so are best

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:The highest concentration of sum TPH was measured in SBA_AUK_BH110, located in the south of SBA and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:27:BTEX. The highest concentrations were measure in SBA_AUK_BH110, located in the south of SBA, and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:27:concentration of 2,100µg/l was measured in SBC_AUK_BH107, to the south of SBA_AUK_BH110 and in the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:27:well locations respectively. Highest concentrations were again measured in SBA_AUK_BH110, with toluene

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:27:concentrations were measured in SBA_AUK_BH110, with sum PAH ranging from 6,000ug/l to 11,000ug/l

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:28:1,400µg/l measured in SBC_AUK_BH107 and a maximum of 690µg/l measured in SBA_AUK_BH110. This

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:highest measured concentration in downgradient monitoring well SBC_AUK_BH110. However, the highest

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:were measured in SBA_AUK_BH110 adjacent to the southern boundary of SBA, which separates SBA from

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:BH110 also had a measured thickness of DNAPL on two of the three groundwater monitoring visits

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:SBA_AUK_ BH110 associated with the Groundwater Source, where contaminants (including hydrocarbons,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent impacts

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: 8,900 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: Aromatic >EC12- 1,600 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: Benzene 2,400 1 47,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: 11,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: 260 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: Anthracene 30 1 52 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: 100 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:36: Monohydric Phenols 2,310 1 16,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:37: 690 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:37: 62,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:37: 31,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:38: Hexavalent Chromium 180 1 280 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:41: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:41:SBA_AUK_BH105, SBA_AUK_BH110, SBC_AUK_BH106, SBC_AUK_BH107, SBC_AUK_BH112 and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:41:SBC_AUK_BH114. SBA_AUK_BH105 and SBA_AUK_BH110 were included in the modelled groundwater

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:41:SBA_AUK_BH110 in relatively close proximity (approximately 70m). SBC_AUK_BH106 is to the east of

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:43:this DQRA, the Groundwater Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:47: SBA_AUK_BH107 SBA_AUK_BH110 SBC_AUK_BH116

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:48: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:48: ( SBC_AUK_TP168 ! SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:49: ! SBA_AUK_BH110 SBC_AUK_TP142

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:49: ! SBC_AUK_BH110 SOUTH TEES

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:50: ! ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:50: SBC_AUK_TP168 SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:51: ! ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:51: ( SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:52: ! SBA_AUK_BH110 SBC_AUK_TP142

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:52: ! SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:53: ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:53: ! SBC_AUK_BH110 SOUTH TEES

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:54: ( SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:54: ( SBC_AUK_BH110 ( SBC_AUK_TP155

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:55: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:56: ( ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:56: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:58: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:60: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:60: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:62: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:62: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:64: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:64: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:66: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:66: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:68: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:68: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:70: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:70: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:72: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:72: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:74: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:74: SBC_AUK_BH110 WELLS SCREENING MADE GROUND (µg/l)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:76: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:76: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:78: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:78: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:94: Adopted Resources BH109 SBC_AUK_BH110 SBC_AUK_BH112 SBC_AUK_BH113

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:5:  Groundwater source in the vicinity of SBC_AUK_BH110 – considered to

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:7: undertaken in this DQRA, the Groundwater Source in the area of SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:18:Dense Non-Aqueous Phase Liquid (DNAPL) was measured in SBA_AUK_BH110 in two of the three

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:18:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent contamination

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:20:contaminant concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110 and the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:21:A NAPL source within the groundwater has been recorded in SBA_AUK_BH110 towards the southern

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:21:plume located north towards the River Tees from the SBA_AUK_BH110 area is present. The NAPL was found

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:21:The groundwater source identified in the vicinity of SBA_AUK_BH110 is considered to form a potentially

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:deposits in SBA_AUK_BH110 at the southern boundary of the site. The NAPL thickness was measured on

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:SBCO area investigation. However, SBA_AUK_BH110 in SBA was the only well from which a measurable

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:include SBA_AUK_BH105 and SBA_AUK_BH110 in the south of SBA where odours, sheen and tar were

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:Higher sum TPH concentrations were measured in SBA_AUK_BH110, but these were saturated so are best

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:The highest concentration of sum TPH was measured in SBA_AUK_BH110, located in the south of SBA and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:27:BTEX. The highest concentrations were measure in SBA_AUK_BH110, located in the south of SBA, and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:27:concentration of 2,100µg/l was measured in SBC_AUK_BH107, to the south of SBA_AUK_BH110 and in the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:27:well locations respectively. Highest concentrations were again measured in SBA_AUK_BH110, with toluene

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:27:concentrations were measured in SBA_AUK_BH110, with sum PAH ranging from 6,000ug/l to 11,000ug/l

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:28:1,400µg/l measured in SBC_AUK_BH107 and a maximum of 690µg/l measured in SBA_AUK_BH110. This

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:highest measured concentration in downgradient monitoring well SBC_AUK_BH110. However, the highest

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:were measured in SBA_AUK_BH110 adjacent to the southern boundary of SBA, which separates SBA from

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:BH110 also had a measured thickness of DNAPL on two of the three groundwater monitoring visits

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:SBA_AUK_ BH110 associated with the Groundwater Source, where contaminants (including hydrocarbons,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent impacts

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: 8,900 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: Aromatic >EC12- 1,600 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: Benzene 2,400 1 47,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: 11,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: 260 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: Anthracene 30 1 52 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: 100 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:36: Monohydric Phenols 2,310 1 16,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:37: 690 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:37: 62,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:37: 31,000 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:38: Hexavalent Chromium 180 1 280 (SBA_AUK_BH110)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:41: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:41:SBA_AUK_BH105, SBA_AUK_BH110, SBC_AUK_BH106, SBC_AUK_BH107, SBC_AUK_BH112 and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:41:SBC_AUK_BH114. SBA_AUK_BH105 and SBA_AUK_BH110 were included in the modelled groundwater

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:41:SBA_AUK_BH110 in relatively close proximity (approximately 70m). SBC_AUK_BH106 is to the east of

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:43:this DQRA, the Groundwater Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:47: SBA_AUK_BH107 SBA_AUK_BH110 SBC_AUK_BH116

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:48: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:48: ( SBC_AUK_TP168 ! SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:49: ! SBA_AUK_BH110 SBC_AUK_TP142

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:49: ! SBC_AUK_BH110 SOUTH TEES

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:50: ! ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:50: SBC_AUK_TP168 SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:51: ! ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:51: ( SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:52: ! SBA_AUK_BH110 SBC_AUK_TP142

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:52: ! SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:53: ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:53: ! SBC_AUK_BH110 SOUTH TEES

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:54: ( SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:54: ( SBC_AUK_BH110 ( SBC_AUK_TP155

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:55: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:56: ( ! SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:56: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:58: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:60: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:60: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:62: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:62: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:64: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:64: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:66: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:66: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:68: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:68: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:70: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:70: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:72: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:72: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:74: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:74: SBC_AUK_BH110 WELLS SCREENING MADE GROUND (µg/l)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:76: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:76: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:78: SBA_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:78: SBC_AUK_BH110

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:94: Adopted Resources BH109 SBC_AUK_BH110 SBC_AUK_BH112 SBC_AUK_BH113

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:5: • Groundwater in the vicinity of BH110 – considered to represent impacts associated

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:6: (BH110 and BH105; location of the highest measured groundwater concentrations of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:6: BH110 and the groundwater source area, from where the highest measured groundwater

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:16:Dense Non-Aqueous Phase Liquid (DNAPL) was measured in BH110 in two of the three groundwater

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:17:A DNAPL source within the groundwater has been measured in BH110 towards the southern boundary of the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:17:the River Tees from the BH110 area is present. The DNAPL was found resting on the boundary between the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:19:Tidal Flats deposits in BH110 at the southern boundary of the site. DNAPL thickness was measured on two

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:concentrations were measured in BH110, but these were saturated so are best represented by groundwater

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:The highest concentration of sum TPH were measured in BH110, located in the south of the site and screening

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:concentrations were measure in BH110, located in the south of the site, and ranged between 24,000 ug/l and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:measured in BH103 and BH105, located in the vicinity of BH110 and screening the Made Ground.

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:were again measured in BH110, with toluene ranging between 2,600ug/l – 4,500ug/l and sum xylenes

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:(2021) were measured in BH110, with sum PAH ranging from 26.9ug/l to 528ug/l across the three visits. The

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:Notwithstanding this, the highest concentrations were distinctly present in BH110 which ranged from <40ug/l

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:is potentially also a separate source relating concentrations in BH110, likely from the SBCO.

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:BH110), suggesting that they relate to a groundwater source rather than the Made Ground. Due to the location

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:unsaturated soils. The highest groundwater contaminant concentrations were measured in BH110 adjacent to

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:measured in nearby location BH105 and downgradient BH103. BH110 also had a measured thickness of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21: • Groundwater in the vicinity of BH110 – considered to represent impacts associated with an off-site

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:The groundwater source area modelled is defined to include BH110 and extends to the west to the edge of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:22:(define as monitoring wells BH105 and BH110) and whether or not they were likely attributable to the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:26:BH110, BH103S and BH2017 all screen the Made Ground. Longitudinal and transverse dispersity were set to

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:26:For the forward prediction, the average concentration of benzene in BH110 was selected as the source

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:26: BH110 Average

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:28:groundwater source area (BH105 and BH110; as discussed in Section 4, generally the locations of the highest

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:29:None of the measured concentrations from either the on-site groundwater source wells (BH110 and BH105;

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:30:decrease, particularly within BH110, where the greatest impacts are observed.

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:34: ! ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:35: ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:36: ! ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:37: 7.7 ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:38: 310 ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:39: 0.1 ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:40: ! ! BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:41: BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:42: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:44: BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:46: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:48: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:50: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:52: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:54: BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:56: BH110 !

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:58: E BH110 @ BH105

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Aromatic C7-C8 74 5900 BH110 Yes1

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Aromatic C16-C21 # 210 BH110 Yes1

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Benzo(k)fluoranthene 0.0000425* 61 BH110 Yes R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Benzo(a)pyrene 0.0000425* 100 BH110 Yes

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Indeno(1,2,3-c,d)pyrene 0.0000425* 74 BH110 Yes R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Dibenzo(a,h)anthracene - 15 BH110 No2 R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Benzo(g,h,i)perylene 0.0000425* 45 BH110 Yes

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Styrene - 43 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:2-chlorotoluene - 2 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:1,3,5-trimethylbenzene - 36 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:Tert-butylbenzene - 8 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:1,2,4-trimethylbenzene - 55 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:60:p-isopropyltoluene - 8 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61:2-Methylphenol - 950 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61:3&4-Methylphenol - 2500 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61:2,4-Dimethylphenol - 880 BH110 No3

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61:Phenol 7.7 1300 BH110 Yes

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61:Cyanide 1 690 BH110 Yes

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:65: _BH110 _BH110 BH110

R-2021-0713-CD-COMPLIANCE OFFICER REPORT.pdf:3:  Groundwater source in the vicinity of SBC_AUK_BH110 – considered to

R-2021-0713-CD-Contam Land.pdf:2:  Groundwater source in the vicinity of SBC_AUK_BH110 – considered to

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:5:  Groundwater source in the vicinity of SBC_AUK_BH110 – considered to

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:7: undertaken in this DQRA, the Groundwater Source in the area of SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:18:Dense Non-Aqueous Phase Liquid (DNAPL) was measured in SBA_AUK_BH110 in two of the three

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:18:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent contamination

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:20:contaminant concentrations beneath SBA would decrease, particularly within SBA_AUK_BH110 and the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:21:A NAPL source within the groundwater has been recorded in SBA_AUK_BH110 towards the southern

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:21:plume located north towards the River Tees from the SBA_AUK_BH110 area is present. The NAPL was found

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:21:The groundwater source identified in the vicinity of SBA_AUK_BH110 is considered to form a potentially

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:deposits in SBA_AUK_BH110 at the southern boundary of the site. The NAPL thickness was measured on

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:SBCO area investigation. However, SBA_AUK_BH110 in SBA was the only well from which a measurable

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:include SBA_AUK_BH105 and SBA_AUK_BH110 in the south of SBA where odours, sheen and tar were

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:Higher sum TPH concentrations were measured in SBA_AUK_BH110, but these were saturated so are best

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:The highest concentration of sum TPH was measured in SBA_AUK_BH110, located in the south of SBA and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:27:highest concentrations were measure in SBA_AUK_BH110, located in the south of SBA, and ranged between

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:27:measured in SBC_AUK_BH107, to the south of SBA_AUK_BH110 and in the vicinity of the SBCO area and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:27:wells respectively. Highest concentrations were again measured in SBA_AUK_BH110, with toluene ranging

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:27:concentrations were measured in SBA_AUK_BH110, with sum PAH ranging from 6,000ug/l to 11,000ug/l

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:28:The maximum total cyanide concentration was measured in BH110 of 690µg/l (<40µg/l to 690µg/l across the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:28:highest measured concentration in downgradient monitoring well SBC_AUK_BH110. However, the highest

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:29:were measured in SBA_AUK_BH110 adjacent to the southern boundary of SBA, which separates SBA from

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:29:BH110 also had a measured thickness of DNAPL on two of the three groundwater monitoring visits

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:29:SBA_AUK_ BH110 associated with the Groundwater Source, where contaminants (including hydrocarbons,

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:29:  Groundwater Source in the vicinity of SBA_AUK_BH110 – considered to represent impacts

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: 5,800 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: Benzene 2,400 1 47,000 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: 25 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: Anthracene 30 1 41,365 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: 2.2 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: Monohydric Phenols 2,310 1 16,000 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:36: 690 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:37: 31,000 (SBA_AUK_BH110)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:38:  SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:38:SBA_AUK_BH105, SBA_AUK_BH110, SBC_AUK_BH106, SBC_AUK_BH107 and SBC_AUK_BH114. Data

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:38:only existed for SBA_AUK_BH105 and SBA_AUK_BH110 at the time of writing the SBA DQRA. These wells

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:38:located south of SBA_AUK_BH105 and SBA_AUK_BH110 in relative close proximity (approximately 70m).

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:40:this DQRA, the Groundwater Source in the area of SBA_AUK_BH110 (interpreted to be associated with the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:44: SBA_AUK_BH107 SBA_AUK_BH110 SBC_AUK_BH116

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:45: SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:47: SBA_AUK_BH110 ! SBC_AUK_BH116

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:49: SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:51: SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:53: SBA_AUK_BH110 SBC_AUK_BH116

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:55: SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:57: SBA_AUK_BH110 SBC_AUK_BH116

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:59: SBA_AUK_BH110 SBC_AUK_BH116

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:61: SBA_AUK_BH110

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:63: SBA_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Glaciolacustrine Deposits), BH108D and BH110 (both screening Mercia Mudstone) on 3rd July 2020. An

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Slug tests were performed on monitoring wells BH101D, BH103, BH108D and BH110, to provide an estimate

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:Rice’s method for a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:126:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:21: Prairie_AUK_BH110 Mercia Mudstone 4.00 3.798

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:49: Prairie_AUK_BH110 Mercia Mudstone

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:50: PRAIRIE_AUK_BH110 180

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:15:(PRAIRIE_AUK_BH110).

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:16:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:18:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:30: PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:31:RIE_AUK_BH110 PRAIRIE_AUK_TP141 Teesside Management Office, Trunk Road,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:32: PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:34:UK_BH110 slotted standpipe

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:61: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:62: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:63: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:64: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: Figure PRAIRIE_AUK_BH110.1

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:65: Figure PRAIRIE_AUK_BH110.2

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:68: Continued as PRAIRIE_AUK_BH110. Advanced to required

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:51: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:52: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:55: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:56: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:61: Sample ID BH108 BH109 BH110 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:62: Sample ID BH108 BH109 BH110 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:69: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:70: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:71: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:86:1668118 PRAIRIE_AUK_BH110 1 3.00 PRAIRIE_AUK_B SOIL NAD none Lee Kerridge

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:100:1668118 PRAIRIE_AUK_BH110 3.00 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:103:1671904 PRAIRIE_AUK_BH110 4.00- 06/05/20 GB 1L x2, GV, PB 1L

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:104:1688256 PRAIRIE_AUK_BH110 3.84- 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:105:1694900 PRAIRIE_AUK_BH110 3.87- 02/07/20 GB 1L, GV, PB 1L, PU

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:8: Prairie_AUK_BH110 Mercia Mudstone 3.8 3.96 3.93 3.84 - 4.00

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:• BH110 - screening Mercia Mudstone

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:three slug insertions) were completed in BH108D and BH110 and four tests (two slug extractions and two slug

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:a partially penetrating well in an unconfined aquifer for BH101D, BH108D and BH110. The hydraulic

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:9:The hydraulic conductivity estimated from the tests conducted in BH108D and BH110 which screen the Mercia

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:11: Prairie_AUK_BH110 Mercia Mudstone 134 1068.3 1235.9

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13: • Prairie_AUK_BH110 (2nd and 3rd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:Concentrations of total cyanide in Prairie_AUK_BH101S/D and Prairie_AUK_BH110 were generally higher

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:than elsewhere. The highest concentration of free cyanide was measured in Prairie_AUK_BH110.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13: • Prairie_AUK_BH110 (2nd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: Prairie_AUK_BH110 Mercia Mudstone

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: Cadmium μg/l 9/36 EQS 0.2 PRAIRIE_AUK_BH110 (2nd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: PRAIRIE_AUK_BH110 (2nd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:18: PRAIRIE_AUK_BH110 (1st and 2nd visits)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: PRAIRIE_AUK_BH110(1st and 3rd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: Total Cyanide μg/l PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:19: PRAIRIE_AUK_BH110 (2nd and 3rd visit)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:20: PRAIRIE_AUK_BH110 (1st and 3rd visits)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:38:(PRAIRIE_AUK_BH110).

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:39:All ten boreholes (PRAIRIE_AUK_BH101 to PRAIRIE_AUK_BH110 inclusive) were installed with monitoring

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:41:PRAIRIE_AUK_BH103, PRAIRIE_AUK_BH108 and PRAIRIE_AUK_BH110 using the Displacement (Slug)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:53: PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:54:RIE_AUK_BH110 PRAIRIE_AUK_TP141 Teesside Management Office, Trunk Road,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:55: PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:57:UK_BH110 slotted standpipe

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:84: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:85: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:86: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:87: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: South Tees Development Corporation PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: Figure PRAIRIE_AUK_BH110.1

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:88: Figure PRAIRIE_AUK_BH110.2

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:91: Continued as PRAIRIE_AUK_BH110. Advanced to required

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part3.PDF:120: PRAIRIE_AUK_BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:82: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:83: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:84: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:139: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:140: Sample ID BH110 SW1 SW2 BH101 BH101

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:143: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:144: Sample ID BH107 BH108 BH108 BH109 BH110

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:149: Sample ID BH108 BH109 BH110 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:150: Sample ID BH108 BH109 BH110 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:157: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:158: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:159: Sample ID BH108 BH110 SW1 SW2 _SW4

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part5.PDF:174:1668118 PRAIRIE_AUK_BH110 1 3.00 PRAIRIE_AUK_B SOIL NAD none Lee Kerridge

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:12:1668118 PRAIRIE_AUK_BH110 3.00 20/04/20 GJ 250ml x2, GJ 60ml x2, PT 1L x2

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:15:1671904 PRAIRIE_AUK_BH110 4.00- 06/05/20 GB 1L x2, GV, PB 1L

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:16:1688256 PRAIRIE_AUK_BH110 3.84- 19/06/20 GB 1L x2, GV, PB 1L, P(other)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:17:1694900 PRAIRIE_AUK_BH110 3.87- 02/07/20 GB 1L, GV, PB 1L, PU

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:290: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:291: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part4.PDF:292: Sample ID TP187 BH110 TP102 TP102 TP103

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part4.PDF:23: PRAIRIE_AUK_BH110