North East File Collection - NEFC

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MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:183:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:183:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:256:iron and steel works, together with industries to support these works (such as fuel storage, tar manufacture

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:264: concrete works a Slag and Tar Macadam Works is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: The Slag and Tar Macadam Work 750m south of the

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: site is now labelled Tar Manufactory.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: connected to the tanks to the south. The Tar Manufactory 750m to the south of the site is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: now labelled Tar Distillation Works and includes multiple

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: There are pipelines travelling from the site tanks and a tar well.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:266:1954 -1958 (OS Not shown The Tar Distillation Works 750m to the south of the site

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:267: An electricity substation has been constructed to The tanks associated with the Tar Distillation Works

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:270:Outside of the site boundary but within the oil depot area, black odorous tar was observed between ground

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:270:corresponds within the black odour tar observed at this location. TPH was not recorded above the DIV

R-2021-0610-PND-SBCO (Phase 2) Demolition.pdf:1: GAS HOLDER AND EQUIPMENT TAR STORAGE TANKS

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:19: Bank ground investigations. Tar and oil

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:15:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:10:iron and steel works, together with industries to support these works (such as fuel storage, tar manufacture

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:18: concrete works a Slag and Tar Macadam Works is

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: The Slag and Tar Macadam Work 750m south of the

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: site is now labelled Tar Manufactory.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: connected to the tanks to the south. The Tar Manufactory 750m to the south of the site is

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: now labelled Tar Distillation Works and includes multiple

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: There are pipelines travelling from the site tanks and a tar well.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:20:1954 -1958 (OS Not shown The Tar Distillation Works 750m to the south of the site

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:21: An electricity substation has been constructed to The tanks associated with the Tar Distillation Works

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:24:Outside of the site boundary but within the oil depot area, black odorous tar was observed between ground

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:24:corresponds within the black odour tar observed at this location. TPH was not recorded above the DIV

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:7: of the tumours induced by coal tar and benzo(a)pyrene in a 2-year bioassay. Carcinogenesis, 19,

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:20: Storage Tanks, Benzole Storage Tanks and Tar Pump House as well as miscellaneous tanks and sub-stations.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:40: power station, gas works and tar works.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:74: site including reservoirs, tar macadam works, water towers, chimneys

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:7: of the tumours induced by coal tar and benzo(a)pyrene in a 2-year bioassay. Carcinogenesis, 19,

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:18: Storage Tanks, Benzole Storage Tanks and Tar Pump House as well as miscellaneous tanks and sub-stations.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:38: power station, gas works and tar works.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:72: site including reservoirs, tar macadam works, water towers, chimneys

R-2021-0166-FFM-Environmental Risk Assessment.pdf:35:and soil leachate analysis indicating that some leaching is occurring from the slag deposits, tar materials,

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:17:protection of human health in groundwater. Non aqueous phase liquid (NAPL) and tar were identified primarily

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:Observations of NAPL and tar were made primarily during intrusive investigation from within the Made

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:Within SBA (excluding SBCO area), observations of NAPL included viscous tar at 0.1-1.3m bgl in

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:25:Within SBB, viscous tar was noted in unsaturated soils from SBB_AUK_TP114, located in the north of the site

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:25:SBCO area, tar and oil were observed in unsaturated Made Ground within SB_AUK_TP103 at 0.9m and

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:12:reclamation, the Redcar Iron and Steel works and small tar works were constructed within the north‐eastern

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:26: Tar and Macadam Works TPH, PAH, ammonia, phenols, pH

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: in S2-TPA08 (4m bgl) located close to the railway lines north of the blast furnace. A tar like odour was

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: hydrocarbons in the C21-C35 range. The impact is noted to be to the north west of the former tar and

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: screening and tar was noted in S2-TPA59. Analysis indicated the contamination was primarily heavy

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: o The impacts are noted to be in the vicinity of the former tar and macadam works shown on

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: a very similar CoC; a TPH concentration of 51,000mg/kg and the presence of tar was noted

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: solid tar like substance had been noted on the Made Ground during excavation of trial pit. Analysis

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30:227,300mg/kg; although tar was noted in this trial pit the concentrations reported do not correspond to the soil

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30:descriptions and Arcadis have concluded the samples was of the tar material only not the wider Made Ground

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:61: S1-TPC10 Tar deposits

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:61: S2-TPA08 Tar odour

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:61: S2-TPA09 Tar in pit/strong creosote odour

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:61: S2-TPA17 Creosote odour and tar in gravel from 3.3m bgl.

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:61: S2-TPA53 Possible tar pockets

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:64: A small tar and macadam works is wastes and asbestos.

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:66: boundaries of when internal corrosion takes place tar vapours, BTEX,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:72: PAOC66 SSI1 Tar lagoons - CH2M desk study High risk Point on-site

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:72: Slag of Tar and area of SSI2

R-2021-1048-FFM-Officer Report 1048.pdf:8:2. Removal of NAPL and tar impacted soils to address risks to Human Health.

R-2021-1048-FFM-Officer Report 1048.pdf:12:shallow soils and additionally from measured concentrations of PAH and tar in

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:5: water bodies. Furthermore it is stated in section 2.7.2 The impact of NAPL and tar is considered in Section

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:5: and tar have been identified within made ground. The

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:5: impact of NAPL and tar on controlled waters quality

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:13: aqueous phase liquids (NAPL) and tar have been identified within made

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:13: ground. The impact of NAPL and tar on controlled waters quality has not

R-2021-1048-FFM-10035117-AUK-XX-XX-CO-ZZ-0486-01-Net_Zero_Rem_Clarification_EA.pdf:15:ensure there is no presence of coal tar. If coal tar is identified this must be

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:8: clay with odour of tar and manure.

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:13: slight tar odour.

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:17: fragments, rare glassy tar and slag.

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:18: clinker. Slight tar odour. Rare scrap metal and wire.

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:37: odour and black layer of coal dust/coal tar fragments.

R-2021-1048-FFM-Earthworks Specification.pdf:20: contaminated with tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:12: and a tar macadam works have been constructed east of the site.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:12: Two additional areas in the north are recorded as slag and tar macadam works.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:13: Further industrial expansion to the east of the site including tar macadam works and slag wool works immediately

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:23:(NAPL) and tar were identified within structures and Made Ground.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24:Isolated hotspots of NAPL and tar were identified within structures and Made Ground. A detailed review of the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:26: Tar Lagoon Tar, PAH, TPH, phenols, SVOC, BTEX

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:29: tar HS(G)661996).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:29: tar piled foundations. tar, as such the risk from these should be

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:30:Mudstone) tar piled foundations.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:31: tar The proposed development as outlined in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:43: Tar Lagoon

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:43: Tar Macadam Works

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:58:9 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:70:12 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:70:B On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:329: on-site and these were the Cleveland Iron Works, Redcar Iron Works, River Tees Dockyard, Tar Distillation Chemical

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:335: Iron Works, River Tees Dockyard, Tar Distillation Chemical Works and South Bank Station – all of which were located

R-2021-1048-FFM-EA_R20211048FFM_OFFICIAL_270122.pdf:5: aqueous phase liquids (NAPL) and tar have been identified within made

R-2021-1048-FFM-EA_R20211048FFM_OFFICIAL_270122.pdf:5: ground. The impact of NAPL and tar on controlled waters quality has not

R-2021-1048-FFM-EA_R20211048FFM_OFFICIAL_270122.pdf:7:ensure there is no presence of coal tar. If coal tar is identified this must be

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:8:coal tar are also present throughout the Made Ground. However, a variety of proven and established

R-2021-1048-FFM-TW-SIZ-XX-JBAU-00-00-RP-EN-0001-S1-P02-NZT_FRA.pdf:12: included a tar plant, made ground with slag up to 10m thick. Site elevations, as noted in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:11: Associated slag wool works and a tar macadam works have been constructed

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:11: 1927 Two additional areas in the north are recorded as slag and tar macadam works. with coke making (if

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:50:9 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:62:12 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:62:B On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:321: on-site and these were the Cleveland Iron Works, Redcar Iron Works, River Tees Dockyard, Tar Distillation Chemical

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:327: Iron Works, River Tees Dockyard, Tar Distillation Chemical Works and South Bank Station – all of which were located

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:16:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:16:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:17:Evidence of non-aqueous phase liquids (NAPL) and Tar have been identified primarily within the Made

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:18:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:18: S2-TPA53 Made Ground Possible tar pockets CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:18: Tar coating on slag and tar AEG 2021

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:24: • Removal of NAPL and tar impacted soils to address risks to Human Health.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:40:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:40:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:4: stocking areas, slag, tar and macadam works, above ground storage tanks, transformers,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:5: Polycyclic Aromatic Hydrocarbons (PAH) and the presence of tar and Non Aqueous Phase

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:5: concentrations of PAH (limited number of locations) and the presence of asbestos and tar /

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:5: be low on the basis that the removal of tar / NAPL is proposed as part of the remedial strategy

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:7: • Tar / NAPL was removed (in line with the Remediation Strategy developed for the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:11:operation, including pellet production, sinter and pellet stocking areas, sinter plant and slag, tar and macadam

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:26:2.7.1 Tar and Non-Aqueous Phase Liquid

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:26: S2-TPA53 Made Ground Possible tar pockets from 2.2m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:27: S2-TPA83 Made Ground Rare glassy black crystalised tar in Made Ground CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:27: MS\BH07 Made Ground Tar coating on slag and tar odour at 4.2m bgl AEG 2022

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:27: Potential solidified tar cladding on buried pipe at

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:27:Visual observation of potential tar and hydrocarbon impacts have been recorded on the Site and are presented

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:33:* Tar was identified in S2-TPA83, described as rare glassy black crystallised tar, within granular Made Ground

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:33:with the tar identified in this location a potential contributing factor to the elevated PAH concentrations identified.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:33:As such, direct contact with shallow soils containing tar (and elevated PAH) in this location may be active.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:33:on-Site industrial workers by the concentrations measured in shallow soils in 12BT14 and potentially tar in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:35:potentially associated with the presence of tar in this location described as “rare glassy black crystallised tar”.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:35:The Made Ground in which the tar was encountered was identified at a minimum depth of 0.3m bgl. PAH were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:35:bgl), although tar was not noted in these locations. The PAH measured represent a potential risk via the direct

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:36:the possible presence of tar from a minimum depth of 0.3m bgl in S2-TPA83 is such that the direct contact

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:vicinity of the former tar and macadam works, iron ponds and steel plant, with a limited number of locations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:The applicable pathways in relation to human health in relation to the tar that was visually identified include the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:depth at which tar has typically been visually identified is such that the direct contact pathways are unlikely to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:represent a significant risk. The exception was tar identified in Made Ground in S2-TPA83, which was identified

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:this location if the tar remained in situ and uncovered.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:It is understood that as part of the remedial strategy for the Site, identified tar and NAPL impacted materials are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:resources in relation to tar / NAPL, albeit a quantitative assessment was not undertaken. However, as part of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:44:the remedial strategy, removal of soils containing tar / NAPL is planned irrespective of potential risks presented.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:45:• Slag, Tar and Macadam works (northern portion of the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:46:• Tar lagoons (southwest of the Site),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:46:Tars and sheens appear to be more prevalent in the north of the Site, in the vicinity of the former tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47: the vicinity of the former iron ponds, tar and macadam plant and steel plant, with similar concentrations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:and PAH correlate with soils in which hydrocarbon odours or tar was noted. Localised hot spots may be present,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:in the northeast of the Site (adjacent to the steel plant). However, it is noted that tar was visually identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:which tar was also visually identified. The second highest concentration of 19,000mg/kg was identified in soil

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:comparatively higher in the northern portion of the Site (in the vicinity of the iron ponds, tar and macadam plant

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51: measured in groundwater collected from the north of the Site in the vicinity of the iron ponds, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:62:from asbestos fibres in shallow soils and additionally from measured concentrations of PAH and tar in a limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:68: Former Slag Tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:253: odour and black layer of coal dust/coal tar fragments.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:422: black rock with iridescent sheen. Possible solidified tar used to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:564:4.20 C N18 2.68 4.65 Mild tar odour).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:564:4.65-5.00 ES8(SL4) (Engineer notes slightly saturated and slag with tar coating).

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:11: Visual and 3.30- Tar noted in gravels.

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:169: at c.3.70m BGL … engineer notes tar present in pit.

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:175: from c.3.30m BGL … black, with much tar in gravel. Very strong creosote odour

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:220: at c.3.70m BGL … engineer notes tar present in pit.

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:226: from c.3.30m BGL … black, with much tar in gravel. Very strong creosote odour

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:10: Possible solidified tar used to

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:161:4.20 C N18 2.68 4.65 Mild tar odour).

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:161:4.65-5.00 ES8(SL4) (Engineer notes slightly saturated and slag with tar coating).

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:352: black rock with iridescent sheen. Possible solidified tar used to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:4: stocking areas, slag, tar and macadam works, above ground storage tanks, transformers,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:5: Polycyclic Aromatic Hydrocarbons (PAH) and the presence of tar and Non Aqueous Phase

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:5: concentrations of PAH (limited number of locations) and the presence of asbestos and tar /

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:5: be low on the basis that the removal of tar / NAPL is proposed as part of the remedial strategy

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:7:  Tar / NAPL was removed (in line with the Remediation Strategy developed for the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:11:operation, including pellet production, sinter and pellet stocking areas, sinter plant and slag, tar and macadam

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:27:2.7.1 Tar and Non-Aqueous Phase Liquid

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: S2-TPA53 Made Ground Possible tar pockets from 2.2m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: of coal dust/coal tar fragments

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: S2-TPA69 Made Ground Tar odour and appearance between 1.8 CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: S2-TPA83 Made Ground Rare glassy black crystalised tar in Made CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: MS\BH07 Made Ground Tar coating on slag and tar odour at 4.2m AEG 2022

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28: Potential solidified tar cladding on buried

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:28:Visual observation of potential tar and hydrocarbon impacts have been recorded on the Site and are presented

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:35:* Tar was identified in S2-TPA83, described as rare glassy black crystallised tar, within granular Made Ground

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:35:with the tar identified in this location a potential contributing factor to the elevated PAH concentrations identified.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:35:As such, direct contact with shallow soils containing tar (and elevated PAH) in this location may be active.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:35:on-Site industrial workers by the concentrations measured in shallow soils in 12BT14 and potentially tar in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:37:potentially associated with the presence of tar in this location described as “rare glassy black crystallised tar”.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:37:The Made Ground in which the tar was encountered was identified at a minimum depth of 0.3m bgl. PAH were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:37:bgl), although tar was not noted in these locations. The PAH measured represent a potential risk via the direct

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:38:the possible presence of tar from a minimum depth of 0.3m bgl in S2-TPA83 is such that the direct contact

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:vicinity of the former tar and macadam works, iron ponds and steel plant, with a limited number of locations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:The applicable pathways in relation to human health in relation to the tar that was visually identified include the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:depth at which tar has typically been visually identified is such that the direct contact pathways are unlikely to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:represent a significant risk. The exception was tar identified in Made Ground in S2-TPA83, which was identified

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:this location if the tar remained in situ and uncovered.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:It is understood that as part of the remedial strategy for the Site, identified tar and NAPL impacted materials are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:resources in relation to tar / NAPL, albeit a quantitative assessment was not undertaken. However, as part of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:46:the remedial strategy, removal of soils containing tar / NAPL is planned irrespective of potential risks presented.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:47: Slag, Tar and Macadam works (northern portion of the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:48: Tar lagoons (southwest of the Site),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:48:Tars and sheens appear to be more prevalent in the north of the Site, in the vicinity of the former tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49: the vicinity of the former iron ponds, tar and macadam plant and steel plant, with similar concentrations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:and PAH correlate with soils in which hydrocarbon odours or tar was noted. Localised hot spots may be present,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:in the northeast of the Site (adjacent to the steel plant). However, it is noted that tar was visually identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:which tar was also visually identified. The second highest concentration of 19,000mg/kg was identified in soil

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:comparatively higher in the northern portion of the Site (in the vicinity of the iron ponds, tar and macadam plant

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53: measured in groundwater collected from the north of the Site in the vicinity of the iron ponds, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:64:from asbestos fibres in shallow soils and additionally from measured concentrations of PAH and tar in a limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:70: Former Slag Tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:85: Tar Project:

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:261: odour and black layer of coal dust/coal tar fragments.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:430: black rock with iridescent sheen. Possible solidified tar used to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:572:4.20 C N18 2.68 4.65 Mild tar odour).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:572:4.65-5.00 ES8(SL4) (Engineer notes slightly saturated and slag with tar coating).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954:MS\BH07 Made Ground Mild tar odour and tar coating on slag between 4.2 and 4.65 m bgl AEG 2022

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954:S2-TPA53 Made Ground Rare pockets of soft black sandy clay with the appearance of tar from 2.2 m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954:S2-TPA59 Made Ground Strong hydrocarbon odour and black layer of coal dust/coal tar fragments CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954:S2-TPA61 Made Ground Possible rare small lumps of coal tar between 0 and 1.2 m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954:S2-TPA69 Made Ground Tar odour and appearance between 1.8 and 2.1 m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:954: Rare black glassy crystallised tar and iron sheet with tar odour between 0.3 and 3.4 m

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:9:hydrocarbons and coal tar are also present throughout the Made Ground. However, a variety of proven

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:26:conditioned the gas for reuse. The treatment removed tar aerosols, ammonia, naphthalene and light oil.

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:26:scrubbers, heat exchangers, naphthalene washers, light tar tanks, heavy tar tanks circulating liquor

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:41: Former Ironworks, Slag & Organics Diesel/Petrol/oil/ coal tar √ √

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:85: GA TAR TAR

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:4: stocking areas, slag, tar and macadam works, above ground storage tanks, transformers,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:5: Polycyclic Aromatic Hydrocarbons (PAH) and the presence of tar and Non Aqueous Phase

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:5: concentrations of PAH (limited number of locations) and the presence of asbestos and tar /

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:5: be low on the basis that the removal of tar / NAPL is proposed as part of the remedial strategy

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:7:  Tar / NAPL was removed (in line with the Remediation Strategy developed for the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:10:operation, including pellet production, sinter and pellet stocking areas, sinter plant and slag, tar and macadam

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:29:* Tar was identified in S2-TPA83, described as rare glassy black crystallised tar, within granular Made Ground

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:29:with the tar identified in this location a potential contributing factor to the elevated PAH concentrations identified.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:29:As such, direct contact with shallow soils containing tar (and elevated PAH) in this location may be active.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:29:on-Site industrial workers by the concentrations measured in shallow soils in 12BT14 and potentially tar in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:31:potentially associated with the presence of tar in this location described as “rare glassy black crystallised tar”.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:31:The Made Ground in which the tar was encountered was identified at a minimum depth of 0.3m bgl. PAH were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:31:bgl), although tar was not noted in these locations. The PAH measured represent a potential risk via the direct

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:32:the possible presence of tar from a minimum depth of 0.3m bgl in S2-TPA83 is such that the direct contact

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:37:vicinity of the former tar and macadam works, iron ponds and steel plant, with a limited number of locations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38: S2-TPA53 Made Ground Possible tar pockets from 2.2m bgl CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38: S2-TPA83 Made Ground Rare glassy black crystalised tar in Made Ground CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38: MS\BH07 Made Ground Tar coating on slag and tar odour at 4.2m bgl AEG 2021

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38: Potential solidified tar cladding on buried pipe at

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:The applicable pathways in relation to human health in relation to the tar that was visually identified include the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:depth at which tar has typically been visually identified is such that the direct contact pathways are unlikely to

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:represent a significant risk. The exception was tar identified in Made Ground in S2-TPA83, which was identified

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:this location if the tar remained in situ and uncovered.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:It is understood that as part of the remedial strategy for the Site, identified tar and NAPL impacted materials are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:39:resources in relation to tar / NAPL, albeit a quantitative assessment was not undertaken. However, as part of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:39:the remedial strategy, removal of soils containing tar / NAPL is planned irrespective of potential risks presented.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:40: Slag, Tar and Macadam works (northern portion of the Site).

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:41: Tar lagoons (southwest of the Site),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:41:Tars and sheens appear to be more prevalent in the north of the Site, in the vicinity of the former tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42: the vicinity of the former iron ponds, tar and macadam plant and steel plant, with similar concentrations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:and PAH correlate with soils in which hydrocarbon odours or tar was noted. Localised hot spots may be present,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:in the northeast of the Site (adjacent to the steel plant). However, it is noted that tar was visually identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:which tar was also visually identified. The second highest concentration of 19,000mg/kg was identified in soil

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:comparatively higher in the northern portion of the Site (in the vicinity of the iron ponds, tar and macadam plant

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46: measured in groundwater collected from the north of the Site in the vicinity of the iron ponds, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:57:from asbestos fibres in shallow soils and additionally from measured concentrations of PAH and tar in a limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:63: Former Slag Tar and

R-2021-1048-FFM-CON LAND 1048.pdf:1:2. Removal of NAPL and tar impacted soils to address risks to Human Health.

R-2021-1048-FFM-MGE04767 Cont Land Response.pdf:2:additionally from measured concentrations of PAH and tar in a limited number of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: Associated slag wool works and a tar macadam works have been constructed

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: 1927 Two additional areas in the north are recorded as slag and tar macadam works. with coke making (if

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:50:9 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:62:12 On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:62:B On site Slag and Tar Macadam Works 1927 1387949

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:321: on-site and these were the Cleveland Iron Works, Redcar Iron Works, River Tees Dockyard, Tar Distillation Chemical

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:327: Iron Works, River Tees Dockyard, Tar Distillation Chemical Works and South Bank Station – all of which were located

R-2021-1048-FFM-Factual Report SSI 1.pdf:68: possible tar deposits

R-2021-1048-FFM-Factual Report SSI 1.pdf:68: tar deposits

R-2021-1048-FFM-Factual Report SSI 1.pdf:69: present (500mmx15mm). Possible slight coal tar odour.

R-2021-1048-FFM-Factual Report SSI 1.pdf:92: coarse angular to subrounded of coke, possible tar and

R-2021-1048-FFM-Factual Report SSI 1.pdf:154: occasional tar cobbles. Brick found at 1.9m

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:17:Evidence of non-aqueous phase liquids (NAPL) and Tar have been identified primarily within the Made

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:18:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:18: S2-TPA53 Made Ground Possible tar pockets CH2M 2017b

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:18: Tar coating on slag and tar AEG 2021

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:24: • Removal of NAPL and tar impacted soils to address risks to Human Health.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:27: indicative NAPL, or tar will be removed to depth as far as reasonably practicable.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:27: indicative NAPL, or tar will be removed to a minimum of 5m beyond the site boundary. A barrier

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:43:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:43:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:6:solidified coal tar and other waste materials has been noted in Area C, with the trial pit logs

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:18:sized fragments were also encountered with extensive evidence of solidified coal tar and some

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:23:logs for Area C which identify “landfill” type material, solidified coal tar material and noxious odours

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:53:Extensive evidence of solidified coal tar and other waste materials has been noted in Area C, with

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:53:boiler ash. Evidence of solidified coal tar has also been reported within the Made Ground beneath

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:53:Area D, consistent with Drawing R/GEN156 which records tar lagoons within the eastern end of this

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:166: possible tar deposits

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:166: tar deposits

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:167: present (500mmx15mm). Possible slight coal tar odour.

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:190: coarse angular to subrounded of coke, possible tar and

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:252: occasional tar cobbles. Brick found at 1.9m

STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part2.pdf:15:0.90 PID 130.0ppm diameter. Black tar with hydrocarbon odour noted probably from

Phase II ESA.pdf:26: Prairie_AUK_TP114 (0.9m bgl) Made Ground Tar noted within and surrounding a clay pipe

Phase II ESA.pdf:26: Prairie_AUK_TP175 (0.6mbgl) Made Ground Tar noted within and surrounding a clay pipe

Phase II ESA.pdf:30: service which was noted to contain tar like material encountered in the trial pit.

Phase II ESA.pdf:56:NAPL and tar has been identified primarily within the Made Ground and associated with subsurface or former

Phase II ESA.pdf:120:0.90 PID 130.0ppm Black tar with hydrocarbon odour noted.

10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:135:0.90 PID 130.0ppm diameter. Black tar with hydrocarbon odour noted probably from

STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:11:target slag or refractory materials as this is considered the responsibility of the developer. NAPL and tar was

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:12:During the site investigation, Non-Aqueous Phase Liquid (NAPL) was observed associated with tar and

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:21:bgl a clay pipe of 12-inch diameter was identified. At the same depth a black tar with a ‘hydrocarbon’ odour

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:22:to remediation due to the presence NAPL and tar: ‘Materials impacted with NAPL and tar should not be

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:NAPL and tar have also been identified at the site and represent a source of concentrations of contaminants

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:NAPL and tar will be treated.

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:26:indicates that the concentrations are associated with tar or NAPL. Under the remediation strategy (Arcadis

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:26:2020b) ‘Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:35: LM LOCALISED TAR / NAPL PERCHED GLACI

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:12:During the site investigation, Non-Aqueous Phase Liquid (NAPL) was observed associated with tar and

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:21:bgl a clay pipe of 12-inch diameter was identified. At the same depth a black tar with a ‘hydrocarbon’ odour

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:22:to remediation due to the presence NAPL and tar: ‘Materials impacted with NAPL and tar should not be

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:NAPL and tar have also been identified at the site and represent a source of concentrations of contaminants

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:NAPL and tar will be treated.

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:26:indicates that the concentrations are associated with tar or NAPL. Under the remediation strategy (Arcadis

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:26:2020b) ‘Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:35: LM LOCALISED TAR / NAPL PERCHED GLACI

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:135:0.90 PID 130.0ppm diameter. Black tar with hydrocarbon odour noted probably from

R-2021-0100-CD-Phase II ESA.pdf:26: Prairie_AUK_TP114 (0.9m bgl) Made Ground Tar noted within and surrounding a clay pipe

R-2021-0100-CD-Phase II ESA.pdf:26: Prairie_AUK_TP175 (0.6mbgl) Made Ground Tar noted within and surrounding a clay pipe

R-2021-0100-CD-Phase II ESA.pdf:30: service which was noted to contain tar like material encountered in the trial pit.

R-2021-0100-CD-Phase II ESA.pdf:56:NAPL and tar has been identified primarily within the Made Ground and associated with subsurface or former

R-2021-0100-CD-Phase II ESA.pdf:120:0.90 PID 130.0ppm Black tar with hydrocarbon odour noted.

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:11:target slag or refractory materials as this is considered the responsibility of the developer. NAPL and tar was

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part2.pdf:15:0.90 PID 130.0ppm diameter. Black tar with hydrocarbon odour noted probably from

R-2021-0753-FFM-Arcadis - South Bank Strategy.pdf:12:Although limited evidence of NAPL and tar have currently been identified within the wider South Bank

R-2021-0753-FFM-Arcadis - South Bank Strategy.pdf:12:of the wider South Bank site. In the wider South Bank site NAPL and Tar have been identified primarily

R-2021-0753-FFM-Arcadis - South Bank Strategy.pdf:12:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:9: of the tumours induced by coal tar and benzo(a)pyrene in a 2-year bioassay. Carcinogenesis, 19,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:22: Storage Tanks, Benzole Storage Tanks and Tar Pump House as well as miscellaneous tanks and sub-stations.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:42: power station, gas works and tar works.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:76: site including reservoirs, tar macadam works, water towers, chimneys

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:330:Works were built on site, with tar processing and manufacturing built adjacent to the sites western

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:330:include Heavy Fuel Oil for combustion, By‐Product Plant products and waste containing coal tar (‘jallop’)

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:331:coal tar are also present throughout the Made Ground. However, a variety of proven and established

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:339: Redcar – Coke Ovens – A96466 (Rev. B) British Steel Corporation – July 1980 (Rev. Details of Tar Decanter

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:339: Tar and Liquor Teesside Division B Sept 1981)

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:340: Tar Decanters –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:340: Proposed Layout of CO10216 Jan 1977 Details of Tar Decanter

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:340: New Tar Decant System Plant

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:340: South Bank ‐ 2No. Tar CO11782 (Rev. C) Service Welding Limited Jan 2000 (Rev. Details of Tar Storage

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:348: Concrete Works are now disused. The Slag and Tar Macadam Works west of the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:348: site has been redeveloped by a new Tar Manufactory, which includes numerous

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:349: southwest corner of the site has been redeveloped into a Tar Distillation Works,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:349: encompassing the adjacent former Tar Manufactory site.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:350: and Tar Pump House as well as miscellaneous tanks and sub‐stations. East of the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:351: The former Tar Distillation Works adjacent to the west of the site have been

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:351: undergoing redevelopment. The former Tar Distillation Works, located adjacent

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:364:  2No. Coal Tar tanks

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:366:  Tar Pump House.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:367:With reference to Drawing W116952 the Tar Decant Facility is located west of the Engineering

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:368:13169 and 7A‐13170. The Breeze Stocking Area currently stockpiles ‘Jallop’, which contains coal tar as

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:368:that materials containing coal tar may present within this area, posing a constraint.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:387:carbonisation plants) the tar and water vapour is removed in condensers, with the tar separated by

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:SBCO and is where coal tar is extracted from the coke oven gas. BTEX, TPH and PAH are found in coal

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:tar, coal and a variety of petroleum products. Given the processes within Area 2, coal tar is considered

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:Fuel Oil Storage Area and wharf are located. These contaminants are found in oil, coal and tar deposits,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:dating from 1899 records a former Slag and Tarmacadam Works, later a Tar Manufactory Works

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:403:likely from coal tar within the By‐Products Plant. Testing in Area D recorded elevated TPH GC which may

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:405: Hydrocarbons – coal tar TPH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:409: Jallop – contains coal tar TPH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:412: Fuel, coke and coal tar Elevated pH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:479: TAR RF

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:651: spent oxide, From gas producers. Coal tar used to bind coal,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:726: 4 ü ü Biological sludge, tar residue, lime slurry,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:740: • B lack odorous tar was observed between depths of 0. 0 to 0.15m bgl in 3AT1

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:814: • Coal tar from gas producers;

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:824: • Coal tar from gas producers;

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:884:Made Ground Biological sludge, tar Site Users Direct contact, Health hazard Unlikely Low

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:18: redeveloped into a Tar Distillation Works

2019s0951 - Energy Recovery Facility Environmental Statement.pdf:105: occupied by ship yards, concrete works, slag works and tar works on the north side of

R-2019-0767-OOM-2019s0951 - Energy Recovery Facility Environmental Statement.pdf:105: occupied by ship yards, concrete works, slag works and tar works on the north side of

R-2021-0725-CD-SUDS AND RIVER RESTORATION PLAN AND SECTION 1 OF 3 (STDC_HWY-ATK-HDG-PR_XS-DR-CD-000001_C02).pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS

R-2021-0725-CD-PROPOSED DRAINAGE LAYOUT SHEET 1 OF 9 - STDC_HWY-ATK-HDG-PR-DR-CD-000002_C01.pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS 8. REFER TO DESIGN RISK REGISTER FOR RESIDUAL HEALTH &

R-2021-0725-CD-SUDS AND RIVER RESTORATION PLAN AND SECTION 3 OF 3 (STDC_HWY-ATK-HDG-PR_XS-DR-CD-000003_C02).pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS

R-2021-0725-CD-PROPOSED DRAINAGE LAYOUT SHEET 6 OF 9 - STDC_HWY-ATK-HDG-PR-DR-CD-000007_C01.pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS 8. REFER TO DESIGN RISK REGISTER FOR RESIDUAL HEALTH &

R-2021-0725-CD-PROPOSED DRAINAGE LAYOUT SHEET 4 OF 9 - STDC_HWY-ATK-HDG-PR-DR-CD-000005_C01.pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS HS/HDG/004 Project Title

R-2021-0725-CD-PROPOSED DRAINAGE LAYOUT SHEET 2 OF 9 - STDC_HWY-ATK-HDG-PR-DR-CD-000003_C01.pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS 8. REFER TO DESIGN RISK REGISTER FOR RESIDUAL HEALTH &

R-2021-0725-CD-SUDS AND RIVER RESTORATION PLAN AND SECTION 2 OF 3 (STDC_HWY-ATK-HDG-PR_XS-DR-CD-000002_C02).pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS

R-2021-0725-CD-PROPOSED DRAINAGE LAYOUT SHEET 3 OF 9 - STDC_HWY-ATK-HDG-PR-DR-CD-000004_C01.pdf:1: HS/HDG/003 - EXISTING TAR BOUND PAVEMENTS 8. REFER TO DESIGN RISK REGISTER FOR RESIDUAL HEALTH &

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:22: spent oxide, From gas producers. Coal tar used to bind coal,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:97: 4 ü ü Biological sludge, tar residue, lime slurry,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:111: • B lack odorous tar was observed between depths of 0. 0 to 0.15m bgl in 3AT1

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:186: • Coal tar from gas producers;

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:196: • Coal tar from gas producers;

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:256:Made Ground Biological sludge, tar Site Users Direct contact, Health hazard Unlikely Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:305: 1.50- Engineer notes tar like

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:305: 2.20- Engineer notes tar like

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:711: 1.50 J4 at c.1.50-1.60m BGL … engineer notes tar like substance pervading soil strata

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:739: 9.384 2.40 at c.2.20-2.40m BGL … black tar like substance covering soil material (sample

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1446:and soil leachate analysis indicating that some leaching is occurring from the slag deposits, tar materials,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: to water treatment plant, concentrations of PAH within the same sample was 27mg/kg. A tar like

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1526: south-east of the site, concentration of PAH within the same sample was 4.2mg/kg. A tar like

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1666: of the tumours induced by coal tar and benzo(a)pyrene in a 2-year bioassay. Carcinogenesis, 19,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1679: Storage Tanks, Benzole Storage Tanks and Tar Pump House as well as miscellaneous tanks and sub-stations.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1699: power station, gas works and tar works.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1733: site including reservoirs, tar macadam works, water towers, chimneys

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:Although limited evidence of NAPL and tar have currently been identified within the South Bank Priority

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:wider South Bank site. In the wider South Bank site NAPL and Tar have been identified primarily within

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-0846-FFM-Arcadis - South Bank Strategy.pdf:12:Although limited evidence of NAPL and tar have currently been identified within the wider South Bank

R-2021-0846-FFM-Arcadis - South Bank Strategy.pdf:12:of the wider South Bank site. In the wider South Bank site NAPL and Tar have been identified primarily

R-2021-0846-FFM-Arcadis - South Bank Strategy.pdf:12:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-0439-CD-South Bank Quay Strategy Rev. 1.pdf:13:NAPL and Tar have locally been identified primarily within the Made Ground and associated with

R-2021-0439-CD-South Bank Quay Strategy Rev. 1.pdf:13:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:99: Asphalting (roofing, Asphalt Unused asphalt containing tar products, contaminated

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:101:containing coal tar Demolition 43.11

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:99: Asphalting (roofing, Asphalt Unused asphalt containing tar products, contaminated

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:101:containing coal tar Demolition 43.11

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:12:During the site investigation, Non-Aqueous Phase Liquid (NAPL) was observed associated with tar and

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:21:bgl a clay pipe of 12-inch diameter was identified. At the same depth a black tar with a ‘hydrocarbon’ odour

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:22:to remediation due to the presence NAPL and tar: ‘Materials impacted with NAPL and tar should not be

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:24:NAPL and tar have also been identified at the site and represent a source of concentrations of contaminants

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:24:NAPL and tar will be treated.

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:26:indicates that the concentrations are associated with tar or NAPL. Under the remediation strategy (Arcadis

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:26:2020b) ‘Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:35: LM LOCALISED TAR / NAPL PERCHED GLACI

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:135:0.90 PID 130.0ppm diameter. Black tar with hydrocarbon odour noted probably from

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:17:Evidence of non-aqueous phase liquids (NAPL) and Tar has been identified primarily within the Made

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:17:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:17: SBA_AUK_TP116 (1.8 – 4.0m bgl) Made Ground Viscous tar noted within soil matrix

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:17:protection of human health in groundwater. Non aqueous phase liquid (NAPL) and tar were identified primarily

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:Observations of NAPL and tar were made primarily during intrusive investigation from within the Made

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:Within SBA (excluding SBCO area), observations of NAPL included viscous tar at 0.1-1.3m bgl in

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:25:Within SBB, viscous tar was noted in unsaturated soils from SBB_AUK_TP114, located in the north of the site

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:25:SBCO area, tar and oil were observed in unsaturated Made Ground within SB_AUK_TP103 at 0.9m and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:17:protection of human health in groundwater. Non aqueous phase liquid (NAPL) and tar were identified primarily

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:Observations of NAPL and tar were made primarily during intrusive investigation from within the Made

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:Within SBA (excluding SBCO area), observations of NAPL included viscous tar at 0.1-1.3m bgl in

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:25:Within SBB, viscous tar was noted in unsaturated soils from SBB_AUK_TP114, located in the north of the site

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:25:SBCO area, tar and oil were observed in unsaturated Made Ground within SB_AUK_TP103 at 0.9m and

R-2021-0713-CD-Arcadis - South Bank Strategy.pdf:12:Although limited evidence of NAPL and tar have currently been identified within the wider South Bank

R-2021-0713-CD-Arcadis - South Bank Strategy.pdf:12:of the wider South Bank site. In the wider South Bank site NAPL and Tar have been identified primarily

R-2021-0713-CD-Arcadis - South Bank Strategy.pdf:12:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:15:the protection of human health in groundwater. NAPL and tar were identified primarily within the Made Ground

R-2021-0713-CD-COMPLIANCE OFFICER REPORT.pdf:2:NAPL and tar were identified primarily within the Made Ground in a couple of

R-2021-0713-CD-Contam Land.pdf:2:NAPL and tar were identified primarily within the Made Ground in a couple of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:17:protection of human health in groundwater. Non aqueous phase liquid (NAPL) and tar were identified primarily

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:Observations of NAPL and tar were made primarily during intrusive investigation from within the Made

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:Within SBA (excluding SBCO area), observations of NAPL included viscous tar at 0.1-1.3m bgl in

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:25:Within SBB, viscous tar was noted in unsaturated soils from SBB_AUK_TP114. The four observations of

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:were noted at base of the Made Ground. Within the SBCO area, tar and oil were observed in unsaturated

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:183:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:256:iron and steel works, together with industries to support these works (such as fuel storage, tar manufacture

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:264: concrete works a Slag and Tar Macadam Works is

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: The Slag and Tar Macadam Work 750m south of the

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: site is now labelled Tar Manufactory.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: connected to the tanks to the south. The Tar Manufactory 750m to the south of the site is

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: now labelled Tar Distillation Works and includes multiple

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:265: There are pipelines travelling from the site tanks and a tar well.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:266:1954 -1958 (OS Not shown The Tar Distillation Works 750m to the south of the site

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:267: An electricity substation has been constructed to The tanks associated with the Tar Distillation Works

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:270:Outside of the site boundary but within the oil depot area, black odorous tar was observed between ground

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:270:corresponds within the black odour tar observed at this location. TPH was not recorded above the DIV

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:183:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:183:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:15:odorous tar was observed in shallow soils within one exploratory hole location within the oil depot boundary.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:10:iron and steel works, together with industries to support these works (such as fuel storage, tar manufacture

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:18: concrete works a Slag and Tar Macadam Works is

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: The Slag and Tar Macadam Work 750m south of the

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: site is now labelled Tar Manufactory.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: connected to the tanks to the south. The Tar Manufactory 750m to the south of the site is

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: now labelled Tar Distillation Works and includes multiple

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:19: There are pipelines travelling from the site tanks and a tar well.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:20:1954 -1958 (OS Not shown The Tar Distillation Works 750m to the south of the site

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:21: An electricity substation has been constructed to The tanks associated with the Tar Distillation Works

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:24:Outside of the site boundary but within the oil depot area, black odorous tar was observed between ground

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:24:corresponds within the black odour tar observed at this location. TPH was not recorded above the DIV

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:13: and a tar macadam works have been constructed east of the site.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:13: Two additional areas in the north are recorded as slag and tar macadam works.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:14: Further industrial expansion to the east of the site including tar macadam works and slag wool works immediately

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:24:(NAPL) and tar were identified within structures and Made Ground.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:25:Isolated hotspots of NAPL and tar were identified within structures and Made Ground. A detailed review of the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:27: Tar Lagoon Tar, PAH, TPH, phenols, SVOC, BTEX

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:30: tar risk by the GQRA / DQRA which will inform

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:30: tar risk by the GQRA / DQRA which will inform

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:31: tar piled foundations.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:31: tar piled foundations. sources of contamination such as NAPL and tar,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:32: tar The proposed development as outlined in

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:32: tar groundwater. sources of contamination such as NAPL and tar,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:47: Tar Lagoon

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:47: Tar Macadam Works

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:68:9 On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:80:12 On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:80:B On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:339: on-site and these were the Cleveland Iron Works, Redcar Iron Works, River Tees Dockyard, Tar Distillation Chemical

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:345: Iron Works, River Tees Dockyard, Tar Distillation Chemical Works and South Bank Station – all of which were located

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: Associated slag wool works and a tar macadam works have been constructed

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: 1927 Two additional areas in the north are recorded as slag and tar macadam works. with coke making (if

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:50:9 On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:62:12 On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:62:B On site Slag and Tar Macadam Works 1927 1387949

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:321: on-site and these were the Cleveland Iron Works, Redcar Iron Works, River Tees Dockyard, Tar Distillation Chemical

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:327: Iron Works, River Tees Dockyard, Tar Distillation Chemical Works and South Bank Station – all of which were located

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:4: stocking areas, slag, tar and macadam works, above ground storage tanks, transformers,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:5: Polycyclic Aromatic Hydrocarbons (PAH) and the presence of tar and Non Aqueous Phase

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:5: concentrations of PAH (limited number of locations) and the presence of asbestos and tar /

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:5: be low on the basis that the removal of tar / NAPL is proposed as part of the remedial strategy

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:7: • Tar / NAPL was removed (in line with the Remediation Strategy developed for the Site).

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:13:operation, including pellet production, sinter and pellet stocking areas, sinter plant and slag, tar and macadam

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:29:2.7.1 Tar and Non-Aqueous Phase Liquid

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: S2-TPA53 Made Ground Possible tar pockets from 2.2m bgl CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: of coal dust/coal tar fragments

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: S2-TPA69 Made Ground Tar odour and appearance between 1.8 CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: S2-TPA83 Made Ground Rare glassy black crystalised tar in Made CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: MS\BH07 Made Ground Tar coating on slag and tar odour at 4.2m AEG 2022

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30: Potential solidified tar cladding on buried

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:30:Visual observation of potential tar and hydrocarbon impacts have been recorded on the Site and are presented

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:37:* Tar was identified in S2-TPA83, described as rare glassy black crystallised tar, within granular Made Ground

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:37:with the tar identified in this location a potential contributing factor to the elevated PAH concentrations identified.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:37:As such, direct contact with shallow soils containing tar (and elevated PAH) in this location may be active.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:37:on-Site industrial workers by the concentrations measured in shallow soils in 12BT14 and potentially tar in

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:39:potentially associated with the presence of tar in this location described as “rare glassy black crystallised tar”.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:39:The Made Ground in which the tar was encountered was identified at a minimum depth of 0.3m bgl. PAH were

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:39:bgl), although tar was not noted in these locations. The PAH measured represent a potential risk via the direct

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:40:the possible presence of tar from a minimum depth of 0.3m bgl in S2-TPA83 is such that the direct contact

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:vicinity of the former tar and macadam works, iron ponds and steel plant, with a limited number of locations

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:The applicable pathways in relation to human health in relation to the tar that was visually identified include the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:depth at which tar has typically been visually identified is such that the direct contact pathways are unlikely to

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:represent a significant risk. The exception was tar identified in Made Ground in S2-TPA83, which was identified

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:this location if the tar remained in situ and uncovered.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:It is understood that as part of the remedial strategy for the Site, identified tar and NAPL impacted materials are

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:resources in relation to tar / NAPL, albeit a quantitative assessment was not undertaken. However, as part of

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:48:the remedial strategy, removal of soils containing tar / NAPL is planned irrespective of potential risks presented.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:49:• Slag, Tar and Macadam works (northern portion of the Site).

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:50:• Tar lagoons (southwest of the Site),

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:50:Tars and sheens appear to be more prevalent in the north of the Site, in the vicinity of the former tar and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51: the vicinity of the former iron ponds, tar and macadam plant and steel plant, with similar concentrations

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:and PAH correlate with soils in which hydrocarbon odours or tar was noted. Localised hot spots may be present,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:in the northeast of the Site (adjacent to the steel plant). However, it is noted that tar was visually identified in

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:which tar was also visually identified. The second highest concentration of 19,000mg/kg was identified in soil

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:comparatively higher in the northern portion of the Site (in the vicinity of the iron ponds, tar and macadam plant

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55: measured in groundwater collected from the north of the Site in the vicinity of the iron ponds, tar and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:66:from asbestos fibres in shallow soils and additionally from measured concentrations of PAH and tar in a limited

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:84: Former Slag Tar and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:102: Tar Project:

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:272: odour and black layer of coal dust/coal tar fragments.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:441: black rock with iridescent sheen. Possible solidified tar used to

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:583:4.20 C N18 2.68 4.65 Mild tar odour).

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:583:4.65-5.00 ES8(SL4) (Engineer notes slightly saturated and slag with tar coating).

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965:MS\BH07 Made Ground Mild tar odour and tar coating on slag between 4.2 and 4.65 m bgl AEG 2022

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965:S2-TPA53 Made Ground Rare pockets of soft black sandy clay with the appearance of tar from 2.2 m bgl CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965:S2-TPA59 Made Ground Strong hydrocarbon odour and black layer of coal dust/coal tar fragments CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965:S2-TPA61 Made Ground Possible rare small lumps of coal tar between 0 and 1.2 m bgl CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965:S2-TPA69 Made Ground Tar odour and appearance between 1.8 and 2.1 m bgl CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:965: Rare black glassy crystallised tar and iron sheet with tar odour between 0.3 and 3.4 m

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:18:Evidence of non-aqueous phase liquids (NAPL) and Tar have been identified primarily within the Made

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:19:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:19: S2-TPA53 Made Ground Possible tar pockets CH2M 2017b

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:19: Tar coating on slag and tar AEG 2021

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:25: • Removal of NAPL and tar impacted soils to address risks to Human Health.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:28: indicative NAPL, or tar will be removed to depth as far as reasonably practicable.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:28: indicative NAPL, or tar will be removed to a minimum of 5m beyond the site boundary. A barrier

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:49:furnaces, coke ovens, biproducts plant, mills, tar and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:49:furnaces, coke ovens, biproducts plant, mills, tar and

R-2021-1058-NM-STDC_HWY-ATK-HKF-PR-DR-CH-000006_C02.pdf:1: HS/HKF/002 - EXISTING TAR BOUND PAVEMENTS SOUTH TEES

R-2021-1058-NM-STDC_HWY-ATK-HPV-PR-DR-CH-000025_C02.pdf:1: REMOVAL OF EXISTING TAR BOUND PAVEMENT

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:8: of the tumours induced by coal tar and benzo(a)pyrene in a 2-year bioassay. Carcinogenesis, 19,

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:21: Storage Tanks, Benzole Storage Tanks and Tar Pump House as well as miscellaneous tanks and sub-stations.

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:44: power station, gas works and tar works.

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:82: site including reservoirs, tar macadam works, water towers, chimneys

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:Although limited evidence of NAPL and tar have currently been identified within the South Bank Priority

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:wider South Bank site. In the wider South Bank site NAPL and Tar have been identified primarily within

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:Materials impacted with NAPL and tar should not be reinstated due to being a primary source of

R-2023-0179-SCP-HyGreen Production Facility Scoping Report_FINAL.pdf:59: white mineralisation/ sulphur mineralisation on slag, localised tar cobbles,

R-2023-0179-SCP-HyGreen Production Facility Scoping Report_FINAL.pdf:61: • Tar Macadam Works;

R-2023-0179-SCP-HyGreen Production Facility Scoping Report_FINAL.pdf:63: • Tar Macadam Works;

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:29: Prairie_AUK_TP114 (0.9m Made Ground Tar noted within and surrounding a clay pipe

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:29: Prairie_AUK_TP175 Made Ground Tar noted within and surrounding a clay pipe

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:30: (AEG 2018 H12] identified a tar like substance in 2 out of 44 intrusive locations.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:34: 1 Non-Aqueous Phase Liquids (NAPL) NAPL, principally oils and tar like substances,

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:37:H5.10 NAPL, principally oils and tar like substances, have been identified with in shallow Made Ground

R-2020-0819-ESM-Dorman Point - Planning Statement - Dec 2020.pdf:52: Liquids (NAPL) principally oils and tar like substances, within shallow Made Ground principally