North East File Collection - NEFC

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EN010103-002424-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Tracked).pdf:142: PAHs exceeded CEFAS Action Level 1 at the majority of sampling stations

EN010103-002424-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Tracked).pdf:142: CEFAS Action Levels than metals and PAHs, although there were instances

EN010103-001586-NZT DCO 8.4 - MMO SoCG - May 2022.pdf:44: that PAH’s and polychlorinated biphenyls (PCBs) have current data available does not provide a complete and project-specific

EN010103-001586-NZT DCO 8.4 - MMO SoCG - May 2022.pdf:44: not preluded sediment from disposal at sea. The PAHs).

EN010103-001586-NZT DCO 8.4 - MMO SoCG - May 2022.pdf:44: action levels of PCBs and PAH’s when compared to the data was intended to provide an early indicative characterisation

EN010103-001586-NZT DCO 8.4 - MMO SoCG - May 2022.pdf:44: trace metals. This is particularly noticeable with PAHs, of the area and key known risks.

EN010103-001064-NZT DCO 6.4.11 ES Vol III Appendix 9C WFD Assessment.pdf:119: PAHs exceeded CEFAS Action Level 1 at the majority of sampling stations

EN010103-001064-NZT DCO 6.4.11 ES Vol III Appendix 9C WFD Assessment.pdf:119: CEFAS Action Levels than metals and PAHs, although there were instances

EN010103-001064-NZT DCO 6.4.11 ES Vol III Appendix 9C WFD Assessment.pdf:130: Phenols after the initial visit, and PAHs and TPHs after the second sampling

EN010103-002235-NZT DCO 8.4 - MMO SoCG (Clean) - Sept 2022(D8).pdf:43: that PAH’s and polychlorinated biphenyls (PCBs) have current data available does not provide a complete and project-specific

EN010103-002235-NZT DCO 8.4 - MMO SoCG (Clean) - Sept 2022(D8).pdf:43: not preluded sediment from disposal at sea. The PAHs).

EN010103-002235-NZT DCO 8.4 - MMO SoCG (Clean) - Sept 2022(D8).pdf:43: action levels of PCBs and PAH’s when compared to the data was intended to provide an early indicative characterisation

EN010103-002235-NZT DCO 8.4 - MMO SoCG (Clean) - Sept 2022(D8).pdf:43: trace metals. This is particularly noticeable with PAHs, of the area and key known risks.

EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:26:hg!Zee!hnk!g^mphkdl,!V^!ln\\^ll_neer!fZgZ`^]!ehp!e^o^el!h_!]^fZg]*! pah!aZo^!lahpg!ln\a!]^]b\Zmbhg!Zg]!\hffbmf^gm!mh!]^ebo^kr!Zg]!

EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:30: pah!^fihp^k! •! C^ebo^k!Zm!Z!`k^Zm^k!

EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:31: hnk!ikh\^ll^l*!lmk^g`ma^g!hnk! Zg]!pZrl!h_!phkdbg`*!bglmbeebg`!Z!\nemnk^!h_!hpg^klabi! d[!gZfj^gZY! pah!^fihp^k*!mZd^!

EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:251:_khf!`Zl!Zg]!^e^\mkb\bmr!nmbebmb^l!Zg]!ma^bk!ZbebZm^l*!Zl!p^ee!Zl!bg]nlmkbZe!\nlmhf^kl! pah!ikhob]^!nl!pbma!\k^]bm!_Z\bebmb^l!fZr!Zelh!_Zbe!mh!i^k_hkf!ng]^k!mahl^!\hgmkZ\ml, EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:252:Zk^!iZb]!_^^l!_hk!ma^bk!l^kob\^l,!Hg!mhmZe*!ma^l^!_^^l!fnlm!ghm!^q\^^]! pahe^!hk!Zgr!iZkm!h_!MZmbhgZe!Fkb]~l!Zll^ml!&pa^ma^k!ma^!Zll^ml!Zk^!h_! EN010103-001605-NZT DCO 9.4 - APPENDIX 6 LATEST AUDITED ACCOUNTS – NATIONAL GRID CARBON LIMITED.pdf:257:Zelh!^!ihlm^',!Sa^k^!p^k^!gh!Zf^g]f^gml!mh*!hk!pZbo^kl!h_*!hnk!Bh]^! pah!Zelh!^g^_bm!_khf!Cbk^\mhkl~!Zg!Nb\^kl~!ebZ[bebmr!bglnkZg\^!\ho^k,

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:12:Table G.11 Summary TPH and PAH Exceedances (DWS) from water ingress into MS\TP06 (grab sample)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:19: On the basis of the limited exceedances of assessment criteria in soil leachate (metals, PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:19: harm or damage to potable water resources. The majority of the soil leachable PAHs are detected

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:19: within the Made Ground in the upper 2.5m bgl. PAHs are generally relatively immobile in the sub-

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:38:Nitrite, PAH 16 Speciated, Total Organic Carbon (TOC), and Hardness

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:83:potential presence of asbestos, pH, acids, alkalis, sulfate, ammonia, cyanides, coal tar, PAH, TPH, VOCs, SVOCs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:83:undertaken by AECOM (AECOM, 2020) indicated high pH, asbestos, isolated occurrences of cyanide, and PAH at

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:83:concentrations which may pose a risk to human health based on a commercial/industrial end use and PAHs (in

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:86:from trial pit MS/TP06 during the works. Organic contamination including speciated hydrocarbons and PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:86:The PAH concentrations identified in the groundwater are generally consistent with the previous ground

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:86:investigations. The majority of the soil leachable PAHs are detected within the Made Ground in the upper 2.5 m

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:86:bgl. PAHs are generally relatively immobile in the sub-surface and in the absence of a mobile non-aqueous free-

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:88:samples for metals, TPH, PAHs, phenols, cyanide and ammoniacal nitrogen. Isolated and sporadic exceedance of

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:98: High pH, fines content (metals, PAHs), Contaminated groundwater

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:101: High pH, fines content (metals, PAHs), h - Determine water level variability

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:236:2. Tar Macadam Works/Redcar Iron & Steel Works - Coal tar PAH/TPH/VOCs/SVOCs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:236:3. Infilled Land – Asbestos, PAH/TPH/VOCs/SVOCs, hazardous ground gas

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:236:4. Railways Land - PAH/TPH/VOCs/SVOCs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240:Wastes – bgl exceeded the screening limit for industrial screening limit for benzo(a)pyrene or other PAHs. Due to the variable nature of

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240: a surrogate for Coal Tar, together with there is a risk that high PAH concentrations may occur in some locations.

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240: Fluoranthene and naphthalene were both Concentrations of one or more PAHs and, in particular, fluoranthene were

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240: excess of their screening criteria protective of comparison with the solubility in water of the higher molecular weight PAHs it was

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240: controlled waters. considered that some or most of the PAH must be attached to suspended solids in

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:240: the water samples. PAHs are generally relatively immobile in the sub-surface and

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:243:Works/Redcar Iron & PAH/TPH/VOCs/SVOCs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:243: PAH/TPH/VOCs/SVOCs Ground workers Moderate/low Moderate/low

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:243:Railways Land PAH/TPH/VOCs/SVOCs Ground workers Moderate/low Moderate/low

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:244:tar, and PAH/TPH/VOCs/SVOCs from the contaminative use activities undertaken at the site.

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:244:undertaken by AECOM indicated high pH, asbestos, isolated occurrences of cyanide, and PAH at concentrations which

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:266:Exceedances of metals, TPH, PAHs, cyanide and ammoniacal nitrogen were detected within the groundwater samples

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:267:The PAH concentrations identified are generally consistent with the previous ground investigations. In general, the

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:267:number of PAH exceedances (fluoranthene) have decreased within the Tidal Flat Deposits during the monitoring

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:268:each of the three rounds. Other PAHs at this location which exceeded in Round 1 (anthracene and benzo(g,h,i)perylene

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:268:The majority of the soil leachable PAHs are detected within the Made Ground in the upper 2.5m bgl. PAHs are generally

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:274:contamination exceedances of the DWS screening value included speciated hydrocarbons and PAHs at concentrations

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:274:Table G.11 Summary TPH and PAH Exceedances (DWS) from water ingress into MS\TP06 (grab sample)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:275:The presence of these elevated hydrocarbons and PAHs within the water encountered within this pit indicates that there

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:275: PAHs (sum of 4) 0.1 15 6 <0.08 1.81 6

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:286: PAHs (sum of 4) mg/kg 0.21 <0.12 <0.12 <0.12 <0.04 <0.12 0.71 1.79 <0.12 - <0.04 0.26 0.22 0.13 <0.12 0.38

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:286: PAH 16 Total mg/kg 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:286: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:290: PAHs (sum of 4) mg/kg <0.12 <0.12 <0.12 0.47 <0.12 0.25 <0.12 <0.12 <0.12 <0.04 <0.12 0.63 1.02 0.5 <0.12 0.12

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:290: PAH 16 Total mg/kg <0.1 <0.1 <0.1 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:290: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:294: PAHs (sum of 4) mg/kg <0.12 0.15 <0.12 0.12 0.29 <0.12 0.24 <0.12 <0.04 <0.12 <0.4 <0.12 <0.12 13.4 0.4 <0.12

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:294: PAH 16 Total mg/kg <0.1 0.61 <0.1 0.3 1.8 <0.1 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:294: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:298: PAHs (sum of 4) mg/kg <0.12 - <0.04 <0.12 <0.12 <0.12 <0.12 <0.12 1.54 <0.12 <0.12 <0.12 1.61 <0.12 0.96 0.047

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:298: PAH 16 Total mg/kg <0.1 - - <0.1 <0.1 0.26 <0.1 <0.1 6.3 0.17 <0.1 <0.1 4 <0.1 3 -

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:298: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:302: PAHs (sum of 4) mg/kg <0.12 <0.12 <0.04 <0.12 <0.12 <0.12 0.53 <0.12 <0.12 <0.04 1.12 <0.04 0.13 <0.12 <0.12 <0.04

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:302: PAH 16 Total mg/kg <0.1 <0.1 - <0.1 <0.1 <0.1 3.1 <0.1 <0.1 <0.1 7 - 0.22 0.16 <0.1 -

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:302: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:306: PAHs (sum of 4) mg/kg 0.73 0.14 0.22 0.059 <0.12 <0.12 <0.4 <0.4 <0.4 1.8 0.7 - - <0.04 <0.4 0.12

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:306: PAH 16 Total mg/kg 2.1 0.56 9.3 - 0.33 <0.1 - - - - - - - - - <0.1

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:306: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:310: PAHs (sum of 4) mg/kg 1.3 0.53 <0.12 <0.12 <0.12 <0.12 0.71 <0.12 0.17 0.94 2.54 1.2 1.44 0.5 0.49 0.13

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:310: PAH 16 Total mg/kg 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32 2.5 5.5 <14.91 2.9 0.44 0.44 <0.1

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:310: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:314: PAHs (sum of 4) mg/kg 0.28 <0.12 <0.12 111 45 <0.04 13.4 0.41 0.06 1.3 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:314: PAH 16 Total mg/kg 2.5 <0.1 <0.1 93 44 <0.1 74 1.8 0.05 7.8 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:314: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: PAHs (sum of 4) µg/L 0.1#2 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: PAH 16 Total µg/L <0.2 0.26 0.61 <0.2 0.63 0.28 0.39 <0.2 0.38 0.36 0.52

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:324: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 0.01 <0.01 <0.01 <0.01 <0.01 0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: PAHs (sum of 4) µg/L 0.1#2 <0.04 <0.04 0.04 <0.04 <0.04 <0.04 <0.04 0.04 <0.04 <0.04 <0.04

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: PAH 16 Total µg/L 0.23 0.22 0.5 0.21 0.76 0.39 0.2 6.8 5.6 1.5 0.42

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:328: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4) #2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 22 2 <0.01 0.01 0.0055 0.005 0.0015 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: PAHs (sum of 4) µg/L 0.1#2 22 2 <0.04 0.04 0.022 0.02 0.0059 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: PAH 16 Total µg/L 22 19 <0.2 6.8 0.93 0.385 1.7 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:332: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:336: PAHs (sum of 4) µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:336: PAH 16 Total µg/L <0.2 0.26 0.61 <0.2 0.63 0.28 0.39 <0.2 0.38 0.36 0.52

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:336: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:340: PAHs (sum of 4) µg/L <0.04 <0.04 0.04 <0.04 <0.04 <0.04 <0.04 0.04 <0.04 <0.04 <0.04

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:340: PAH 16 Total µg/L 0.23 0.22 0.5 0.21 0.76 0.39 0.2 6.8 5.6 1.5 0.42

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:340: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:344: PAHs (sum of 4) µg/L 22 2 <0.04 0.04 0.022 0.02 0.0059 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:344: PAH 16 Total µg/L 22 19 <0.2 6.8 0.93 0.385 1.7 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:344: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:350: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:354: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:358: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:362: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:366: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:370: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:373: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:373:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:373: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:374: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:374: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:377: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:377:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:377: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:378: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:378: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:381: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:381:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:381: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:382: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:382: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:385: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:385:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:385: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:386: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:386: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:389: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:389:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:389: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:390: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:390: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:393: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:393:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:393: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:394: Use PAHs

EN010103-001738-NZT DCO 9.8 Appendix GH.1.1b Preliminary Onshore Ground Investigation for GIR Report - June 2022.pdf:394: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-002067-NZT DCO 8.4 - Marine Management Organisation SoCG (Tracked) August 2022 (D6).pdf:44: that PAH’s and polychlorinated biphenyls (PCBs) have current data available does not provide a complete and project-specific

EN010103-002067-NZT DCO 8.4 - Marine Management Organisation SoCG (Tracked) August 2022 (D6).pdf:44: not preluded sediment from disposal at sea. The PAHs).

EN010103-002067-NZT DCO 8.4 - Marine Management Organisation SoCG (Tracked) August 2022 (D6).pdf:44: action levels of PCBs and PAH’s when compared to the data was intended to provide an early indicative characterisation

EN010103-002067-NZT DCO 8.4 - Marine Management Organisation SoCG (Tracked) August 2022 (D6).pdf:44: trace metals. This is particularly noticeable with PAHs, of the area and key known risks.

EN010103-001603-NZT DCO 9.4 - APPENDIX 4 LATEST AUDITED ACCOUNTS – SHELL U.K. LIMITED.pdf:338:Shell Exploration et Production du Maroc GmbH a 100 Shell Pahal Social Welfare Association a 100

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:2: PAHs (sum of 4) mg/kg 0.21 <0.12 <0.12 <0.12 <0.04 <0.12 0.71 1.79 <0.12 - <0.04 0.26 0.22 0.13 <0.12 0.38

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:2: PAH 16 Total mg/kg 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:2: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:6: PAHs (sum of 4) mg/kg <0.12 <0.12 <0.12 0.47 <0.12 0.25 <0.12 <0.12 <0.12 <0.04 <0.12 0.63 1.02 0.5 <0.12 0.12

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:6: PAH 16 Total mg/kg <0.1 <0.1 <0.1 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:6: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:10: PAHs (sum of 4) mg/kg <0.12 0.15 <0.12 0.12 0.29 <0.12 0.24 <0.12 <0.04 <0.12 <0.4 <0.12 <0.12 13.4 0.4 <0.12

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:10: PAH 16 Total mg/kg <0.1 0.61 <0.1 0.3 1.8 <0.1 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:10: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:14: PAHs (sum of 4) mg/kg <0.12 - <0.04 <0.12 <0.12 <0.12 <0.12 <0.12 1.54 <0.12 <0.12 <0.12 1.61 <0.12 0.96 0.047

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:14: PAH 16 Total mg/kg <0.1 - - <0.1 <0.1 0.26 <0.1 <0.1 6.3 0.17 <0.1 <0.1 4 <0.1 3 -

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:14: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:18: PAHs (sum of 4) mg/kg <0.12 <0.12 <0.04 <0.12 <0.12 <0.12 0.53 <0.12 <0.12 <0.04 1.12 <0.04 0.13 <0.12 <0.12 <0.04

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:18: PAH 16 Total mg/kg <0.1 <0.1 - <0.1 <0.1 <0.1 3.1 <0.1 <0.1 <0.1 7 - 0.22 0.16 <0.1 -

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:18: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:22: PAHs (sum of 4) mg/kg 0.73 0.14 0.22 0.059 <0.12 <0.12 <0.4 <0.4 <0.4 1.8 0.7 - - <0.04 <0.4 0.12

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:22: PAH 16 Total mg/kg 2.1 0.56 9.3 - 0.33 <0.1 - - - - - - - - - <0.1

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:22: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:26: PAHs (sum of 4) mg/kg 1.3 0.53 <0.12 <0.12 <0.12 <0.12 0.71 <0.12 0.17 0.94 2.54 1.2 1.44 0.5 0.49 0.13

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:26: PAH 16 Total mg/kg 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32 2.5 5.5 <14.91 2.9 0.44 0.44 <0.1

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:26: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:30: PAHs (sum of 4) mg/kg 0.28 <0.12 <0.12 111 45 <0.04 13.4 0.41 0.06 1.3 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:30: PAH 16 Total mg/kg 2.5 <0.1 <0.1 93 44 <0.1 74 1.8 0.05 7.8 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:30: Benzo(a)pyrene (surrogate marker for PAH mixture)

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: PAHs (sum of 4) µg/L 0.1#2 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: PAH 16 Total µg/L <0.2 0.26 0.61 <0.2 0.63 0.28 0.39 <0.2 0.38 0.36 0.52

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:40: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 0.01 <0.01 <0.01 <0.01 <0.01 0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: PAHs (sum of 4) µg/L 0.1#2 <0.04 <0.04 0.04 <0.04 <0.04 <0.04 <0.04 0.04 <0.04 <0.04 <0.04

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: PAH 16 Total µg/L 0.23 0.22 0.5 0.21 0.76 0.39 0.2 6.8 5.6 1.5 0.42

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:44: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: Indeno(1,2,3-c,d)pyrene µg/L 9E99 Use PAHs (sum of 4) #2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: Benzo(g,h,i)perylene µg/L 9E99 Use PAHs (sum of 4)#2 22 2 <0.01 0.01 0.0055 0.005 0.0015 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: Benzo(b)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: Benzo(k)fluoranthene µg/L 9E99 Use PAHs (sum of 4)#2 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: PAHs (sum of 4) µg/L 0.1#2 22 2 <0.04 0.04 0.022 0.02 0.0059 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: PAH 16 Total µg/L 22 19 <0.2 6.8 0.93 0.385 1.7 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:48: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:52: PAHs (sum of 4) µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:52: PAH 16 Total µg/L <0.2 0.26 0.61 <0.2 0.63 0.28 0.39 <0.2 0.38 0.36 0.52

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:52: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:56: PAHs (sum of 4) µg/L <0.04 <0.04 0.04 <0.04 <0.04 <0.04 <0.04 0.04 <0.04 <0.04 <0.04

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:56: PAH 16 Total µg/L 0.23 0.22 0.5 0.21 0.76 0.39 0.2 6.8 5.6 1.5 0.42

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:56: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:60: PAHs (sum of 4) µg/L 22 2 <0.04 0.04 0.022 0.02 0.0059 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:60: PAH 16 Total µg/L 22 19 <0.2 6.8 0.93 0.385 1.7 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:60: Benzo(a)pyrene (surrogate marker for PAH mixture) µg/L 22 0 <0.01 <0.01 0.005 0.005 0 0 0

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:66: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:70: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:74: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:78: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:82: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:86: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:89: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:89:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:89: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:90: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:90: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:93: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:93:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:93: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:94: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:94: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:97: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:97:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:97: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:98: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:98: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:101: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:101:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:101: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:102: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:102: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:105: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:105:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:105: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:106: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:106: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:109: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:109:Sum of 4 PAHs <0.024 ug/l 40 0 <0.024 <0.024 <0.024 0.1 WS Regs 2016 (Eng/Wal) NO 0 <0.024

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:109: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:110: Use PAHs

EN010103-001740-NZT DCO 9.8 Appendix GH.1.1b Appendix I Screening Tables - June 2022.pdf:110: n/US Non suitable sample. PAH concentrations to high to undertake low level PAH analysis

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:385: PAHs

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:394: PAHs

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:403: PAHs

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:413: PAHs

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:422: PAHs

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:444: PAHs by GC-MS.

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:444: low level PAHs by GC-MS HES.

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:492:Subcontracted PAH's

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:492:Subcontracted PAH's Low Levl

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:495:Subcontracted PAH's

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:495:Subcontracted PAH's Low Levl

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:498:Subcontracted PAH's

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:498:Subcontracted PAH's Low Levl

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:510: PAH Glass 20g EPA Victoria 14 days -

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:511: PAH Glass 500 ISO 5667 3:2018 none 4 days

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: Soils and associated materials are extracted in dichloromethane (DCM) using sonication. The PAH concentration

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: is recorded both as “Total PAH” and as “Speciated PAH”, specified in terms of the 16 US EPA “Priority In-house method based on US EPA Method 8100, Polynuclear Aromatic

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: DETSC 3301 PAH in Soil by GC-FID UKAS (16 PAH's only)

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: 1.6 mg/kg Total PAH

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: Soils are extracted into hexane: acetone by shaking. The PAH concentration is recorded both as “Total PAH” and

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: as “Speciated PAH”, specified in terms of the 16 US EPA “Priority Pollutant” Polycyclic Aromatic In-house method based on US EPA Method 8100, Polynuclear Aromatic

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: DETSC 3302 Hexane / Acetone Extracted PAH in Soil by GC-FID Not Accredited

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: 1.6 mg/kg Total PAH

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: The PAHs in the soil sample are extracted into hexane: acetone by shaking. The PAHs in the extract are separated UKAS (All 16 PAH's)

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: by gas chromatography and identified by the mass selective detector. The concentration of each PAH is

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: (GC/MS) 0.10 mg/kg Total PAH

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: The PAHs in the water sample are extracted into dichloromethane by shaking. The PAHs in the extract are Semivolatile Organic Compounds by Gas Chromatography – Mass Spectrometry

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: separated by gas chromatography and identified by the mass selective detector. The concentration of each PAH is (GC/MS).

EN010103-001744-NZT DCO 9.8 Appendix GH.1.1a Factual Report Part 16 - June 2022.pdf:523: DETSC 3304 Polyaromatic Hydrocarbons in Waters by GC-MS 10 ng/l each UKAS (16 PAH's only)

EN010103-002066-NZT DCO 8.4 - Marine Management Organisation SoCG (Clean) August 2022 (D6).pdf:44: that PAH’s and polychlorinated biphenyls (PCBs) have current data available does not provide a complete and project-specific

EN010103-002066-NZT DCO 8.4 - Marine Management Organisation SoCG (Clean) August 2022 (D6).pdf:44: not preluded sediment from disposal at sea. The PAHs).

EN010103-002066-NZT DCO 8.4 - Marine Management Organisation SoCG (Clean) August 2022 (D6).pdf:44: action levels of PCBs and PAH’s when compared to the data was intended to provide an early indicative characterisation

EN010103-002066-NZT DCO 8.4 - Marine Management Organisation SoCG (Clean) August 2022 (D6).pdf:44: trace metals. This is particularly noticeable with PAHs, of the area and key known risks.

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:3:Works / Redcar PAH/TPH/VOC/SVO GI

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:4: PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:4:Railway Land PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:4: PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:5:(Coking) Works PAH/TPH/VOC/SVO GI

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:5: PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:5: PAH/TPH/VOC/SVO GI

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:5:Railways Land PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:5:Haverton Hill PAH/TPH/VOCs/SV Groundworkers Moderate GI

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:6: PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:6:Railways Land PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:6: PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001107-NZT DCO 6.4.14 ES Vol III Appendix 10C Contaminated Land Environmental Risk Assessment.pdf:6:Railways Land PAH/TPH/VOC/SVO Ground workers Moderate/low Management solution

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:17:14.3.7 Where available, PAH concentrations were compared to Effects Range Low

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:18:14.3.10 Concentrations of PAHs were considerably higher at stations 1 and 2

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:18: concentrations of PAHs were below the standards presented, with the

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:18:14.3.11 As with PAHs and trace metals, levels of THC at stations 1 and 2 were

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:27: content of mud, sand, and gravel, trace metals, and PAHs. Due to the

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:27: analysed. The Global BEST Test found that a combination of the PAHs

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:27:14.3.31 Stations 1 and 2 exhibited elevated levels of PAHs compared to other

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37: levels of both trace metals and PAHs identified at stations 1 and 2, in the

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37:14.4.13 The concentrations of PAHs were compared against the sediment chemical

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37: sites analysed PAHs were also elevated (e.g. chrysene between 259 – 2,470

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37: PAHs can have toxic effects on infaunal communities, which can lead to long

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37: (Papageorgiou et al., 2006). The concentration of PAH, particularly the

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:37: trace metals and PAHs adhere to sediment particles and are rapidly

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:39: Elevated levels of PAHs and trace metals were recorded at stations 1 and 2,

EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf:50:Table C-2: PAH sediment concentrations against Canadian guidelines (CCME, 1999) and ERLs/ ERMs (Long et al., 1995)

EN010103-001838-Environment Agency - Comments on any other information submitted at Deadline 2.pdf:7:compounds of Speciated PAH (Benzo(b)fluoranthene, Benzo(k)fluoranthene,

EN010103-001838-Environment Agency - Comments on any other information submitted at Deadline 2.pdf:7:Section 24.5.3 G.5.3 (Discussion) states that PAH compounds are generally

EN010103-001838-Environment Agency - Comments on any other information submitted at Deadline 2.pdf:7:site. We do not agree wholly with this comment, since it is apparent that PAH

EN010103-002423-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Clean).pdf:136: PAHs exceeded CEFAS Action Level 1 at the majority of sampling stations

EN010103-002423-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Clean).pdf:136: CEFAS Action Levels than metals and PAHs, although there were instances

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:21:14.3.22 Concentrations of a range of PAHs as well as THC for all 10 sampling

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:21: stations are presented in Annex C. Where available, PAH concentrations

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:22:14.3.25 Samples from all 10 sampling stations had a PAH concentration below

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:30: individual PAH, Organotin, PCB and Organochlorine concentrations which

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:32: 5, but no other heavy/trace metals, PAHs, PCBs, Organotins or

EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf:63:Table C-2 PAH sediment concentrations against Canadian guidelines (CCME, 1999) and ERLs/ ERMs (Long et al., 1995)

EN010103-002236-NZT DCO 8.4 - MMO SoCG (Tracked) - Sept 2022(D8).pdf:44: that PAH’s and polychlorinated biphenyls (PCBs) have current data available does not provide a complete and project-specific

EN010103-002236-NZT DCO 8.4 - MMO SoCG (Tracked) - Sept 2022(D8).pdf:44: not preluded sediment from disposal at sea. The PAHs).

EN010103-002236-NZT DCO 8.4 - MMO SoCG (Tracked) - Sept 2022(D8).pdf:44: action levels of PCBs and PAH’s when compared to the data was intended to provide an early indicative characterisation

EN010103-002236-NZT DCO 8.4 - MMO SoCG (Tracked) - Sept 2022(D8).pdf:44: trace metals. This is particularly noticeable with PAHs, of the area and key known risks.

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:11: metals, inorganics, petroleum hydrocarbons including TPH and PAHs were

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:11: aromatic hydrocarbons, TPH, BTEX, PCBs, US 16 EPA PAH, VOCs,

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:11: PAHs were also determined.

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:12: hydrocarbons, TPH, BTEX, PCBs, US 16 EPA PAH, VOCs and SVOCs were

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:12: including TPH, PAHs, PCBs, asbestos identification and quantification. A

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:12: PAHs were measured. X-ray fluorescence (XRF) analysis was undertaken

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:15: PAH in granular Made Ground. Concentrations in natural deposits

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:15: (crushed samples of) Made Ground. TPH and PAH were also

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:23: contaminants of concern including metals, and PAHs to groundwater

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:212: concentrations of PAHs. Where high PAHs are present appropriate

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:219: engines and heating plant, e.g. ash and clinker containing metals and PAHs.

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:220: wastes from coal reforming and combustion (principally PAHs), ammonia

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:221: acids, alkalis, metals, metalloids, asbestos, sulphur compounds, PAHs

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:223: PAHs: ash storage/disposal, waste oil storage, waste disposal sites, gasworks areas.

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:224: drivers are considered to be PAHs including benzo(a)pyrene, which is used

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:227: PAHs Χ

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:228: and combustion products (TPH, PAH), alkali (e.g. clinker), sulphate,

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:229: and combustion products (TPH, PAH), alkali (e.g. clinker), acid (e.g.

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:229: PAHs), PCBs used as dielectrics in electrical transformers, construction and

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:246:10.10.100 A Moderate risk from exposure to PAH / TPH / VOCs / SVOCs has been

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:246:10.10.101 A Moderate risk from exposure to PAH / TPH has been assessed for future

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:247: from PAH / TPH on railway land and infilled ground. This risk affects most

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:247: receptors from leaching of TPH / PAH in the PCC Site and the Water

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:247: materials and utilities from TPH / PAH / VOCs / SVOCs in soil and

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:251:Iron & Steel Works PAH / TPH / VOCs / SVOCs Ground investigation

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:252: PAH / TPH /VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:252:Railways Land PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:253: PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:253: PAH / TPH / VOCs / SVOCs Ground investigation

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:254: PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:254: PAH / TPH / VOCs / SVOCs Ground investigation

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:254:Railways Land PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:254: PAH / TPH / VOCs / SVOCs Groundworkers Moderate Ground investigation

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:255: PAH / TPH /VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:255:Railways Land PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:256: PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-001073-NZT DCO 6.4.12 ES Vol III Appendix 10A PSSR.pdf:256:Railways Land PAH / TPH / VOCs / SVOCs Ground workers Moderate / low Management solution

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:19:notes that PAH’s and polychlorinated Development.

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:19:levels of PCBs and PAH’s when

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:19:particularly noticeable with PAHs,

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:20:metals, organotins and PAHs.

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:49: and polycyclic aromatic hydrocarbon (PAH) concentrations. Metals and PAHs

EN010103-000895-NZT DCO 6.2.9 ES Vol I Chapter 9 Surface Water, Flood Risk and Water Resources.pdf:49: Levels than metals and PAHs, although there were instances of exceedances

EN010103-001912-NZT DCO 9.17 - Hydrogeological Impact Assessment July 2022 (D4).pdf:3: PAH Polycyclic Aromatic Hydrocarbons

EN010103-001912-NZT DCO 9.17 - Hydrogeological Impact Assessment July 2022 (D4).pdf:20:2.4.18 In the previous ground investigations hydrocarbons (TPH and PAHs) were detected

EN010103-001912-NZT DCO 9.17 - Hydrogeological Impact Assessment July 2022 (D4).pdf:20:2.4.21 PAHs were present mainly in the upper 2.5m of the made ground/fill and were shown

EN010103-001912-NZT DCO 9.17 - Hydrogeological Impact Assessment July 2022 (D4).pdf:22: is no evidence of any significant contamination as TPHs, PAHs, VOCs and SVOCs were

EN010103-001114-NZT DCO 6.4.13 ES Vol III Appendix 10B Contaminated Land- Conceptual Site Model.pdf:5: heating plant, e.g. ash and clinker containing metals and PAHs. As well as using Durham coal some salt pans are reported

EN010103-001114-NZT DCO 6.4.13 ES Vol III Appendix 10B Contaminated Land- Conceptual Site Model.pdf:5: (principally PAHs), ammonia liquors and ammonium salts, , metals, acids, alkalis, naphtha, fuel oils, PCBs, asbestos.

EN010103-001114-NZT DCO 6.4.13 ES Vol III Appendix 10B Contaminated Land- Conceptual Site Model.pdf:7: contaminated with harmful TPH / PAHs), PCBs used as dielectrics in electrical transformers and construction and

EN010082-000177-EN010082-6.2.6-ES Chapter 6-Ground Conditions, Water Resources and Flooding-Final-November 2017.pdf:35: hydrocarbons and PAH were present in the groundwater underlying the

EN010082-000177-EN010082-6.2.6-ES Chapter 6-Ground Conditions, Water Resources and Flooding-Final-November 2017.pdf:35: a range of PAH and aliphatic and aromatic TPH fractions were reported in

EN010082-000194-EN010082-6.3.4-ES Annex D1-Phase 1 Final-November 2017.pdf:15:  Concentrations of metals, sulphate, petroleum hydrocarbons and PAH

EN010082-000194-EN010082-6.3.4-ES Annex D1-Phase 1 Final-November 2017.pdf:15: metals (specifically Chromium VI, and selenium) a range of PAH and

EN010082-000194-EN010082-6.3.4-ES Annex D1-Phase 1 Final-November 2017.pdf:24: concentrations of metals, TPH, SVOCs (carbazole) and PAH were detected

EN010082-000194-EN010082-6.3.4-ES Annex D1-Phase 1 Final-November 2017.pdf:25: metals, sulphate, petroleum hydrocarbons and PAH were detected in

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:18:x In soil, low concentrations of metals, TPH, SVOCs (carbazole) and PAH were detected.

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:18:x In groundwater, concentrations of metals, sulphate, TPH and PAH exceeded laboratory

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:18: metals (hexavalent chromium and selenium), a range of PAH and aliphatic and aromatic

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:49:concentrations exceeding laboratory method detection limits for PAHs in two samples and

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:54:Concentrations of metals, sulphate, TPH and PAH exceeded laboratory method detection

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:55:chromium and selenium), a range of PAH and aliphatic and aromatic fractions of TPH were

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:58:a diagonal line from centre south to north-west. The maximum total PAH detected was 8.9

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:66: PAH in the soil. contaminated soils, workers ENVIRON’s GACs for a commercial / industrial end use.

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:69: x In soil, low concentrations of metals, TPH, SVOCs (carbazole) and PAH were

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:69: x In groundwater, concentrations of metals, sulphate, TPH and PAH exceeded

EN010082-000196-EN010082-6.3.6-ES Annex D3-Site Condition Report-Final-November 2017.pdf:69: PAH and aliphatic and aromatic fractions of TPH were found to exceed the relevant UK

EN010082-000501-8.9 - Tees CCPP - Abbreviation List.pdf:7: PAH Polycyclic Aromatic Hydrocarbons

EN010082-000191-EN010082-6.3.1-ES Annex A-Scoping Report-Final-November 2017.pdf:66:  Low concentrations of metals, TPH, SVOCs (carbazole) and PAH were

EN010082-000191-EN010082-6.3.1-ES Annex A-Scoping Report-Final-November 2017.pdf:66:  Concentrations of metals, sulphate, TPH and PAH exceeded laboratory

EN010082-000191-EN010082-6.3.1-ES Annex A-Scoping Report-Final-November 2017.pdf:66: chromium and selenium), a range of PAH and aliphatic and aromatic

EN010082-000019-Scoping Report.pdf:64:  Low concentrations of metals, TPH, SVOCs (carbazole) and PAH were

EN010082-000019-Scoping Report.pdf:64:  Concentrations of metals, sulphate, TPH and PAH exceeded laboratory

EN010082-000019-Scoping Report.pdf:64: chromium and selenium), a range of PAH and aliphatic and aromatic

TR030002-000468-Section 6 App 6.2 Land Quality Generic Risk Assessment.pdf:36: Carbon Banded and Aliphatic/Aromatic Split, PAH 16, Phenol, Asbestos, Volatile

TR030002-000460-Section 3 App 3.1 Waste management.pdf:63: PAHs, TPH and tin compounds are substances and, therefore, a worst case assessment is not

TR030002-000460-Section 3 App 3.1 Waste management.pdf:64: of the PAH determinands. This process involves calculating the ratio of the bap concentration

TR030002-000460-Section 3 App 3.1 Waste management.pdf:65: adverse effects in the aquatic environment. Some PAHs and organo-tin compounds also have

TR030002-000460-Section 3 App 3.1 Waste management.pdf:65:1.7.17 Two PAH substances have ecotoxic substance specific thresholds. These are

TR030002-000460-Section 3 App 3.1 Waste management.pdf:73: aromatic hydrocarbons (PAHs) within the TPH in the waste. Several PAHs are carcinogenic,

TR030002-000460-Section 3 App 3.1 Waste management.pdf:73: and that these generally give oil carcinogenic properties. The PAH used as a carcinogenic

TR030002-000460-Section 3 App 3.1 Waste management.pdf:83:The key properties with the lowest threshold are very toxic (H6 certain heavy metals and organics), carcinogenic (H7 TPH and PAH), toxic for reproduction (H10 for lead) and ecotoxic (H14, PAH and heavy metals).

TR030002-000460-Section 3 App 3.1 Waste management.pdf:101:TPH and PAH Assessment

TR030002-000460-Section 3 App 3.1 Waste management.pdf:101:Carcinogenic PAH

TR030002-000460-Section 3 App 3.1 Waste management.pdf:111:Carcinogenic PAH

TR030002-000460-Section 3 App 3.1 Waste management.pdf:118:9 of the USEPA 16 priority PAHs are also similarly ecotoxic (indicated in green highlight).

TR030002-000460-Section 3 App 3.1 Waste management.pdf:118:Ecotoxic PAH (if < LoD, enter the result as the LoD value ) A01 A02 A03 A04 A05 A06 A07 A08

TR030002-000460-Section 3 App 3.1 Waste management.pdf:124: Total EPA16 Priority PAH µg/kg 12400 19600 239 481 10700 2720 57800 115000

TR030002-000566-Doc 7.1 Planning Statement.pdf:90: elevated concentrations of both heavy metals and PAHs in the study

TR030002-000462-Section 4 App 4.1 Environmental Scoping Report.pdf:8: PAH Polyaromatic Hydrocarbons

TR030002-000561-Doc 6.7 Environmental Statement Non Technical Summary_2 of 2.pdf:14: identified metal and PAH concentrations in estuarine sediments which exceed Cefas Action Levels 1

TR030002-000441-ES Section 6 Hydrology_hydrogeology_land quality.pdf:18: obtained and analysed. not available) were also noted for nickel(2), boron(4), PAHs(1),

TR030002-000074-131202_TR030002_York Potash Harbour Facilities_Scoping Report.pdf:6: PAH Polyaromatic Hydrocarbons

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:14: metals and PAHs were recorded.

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:14:7.4.13 The PAH and total PCB concentrations have also been compared to Cefas Action Levels (PAHs have

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:14: been compared to the indicative PAH Action Levels). This data indicates that the majority of the

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:14: sampling stations exceed Cefas Action Level 1 for concentrations of PAHs at varying depths. There

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:14: Level 1 at VC06, VC05 and VC03. When compared to the CSQG, only a small number of PAH

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:31: concentrations of both heavy metals and PAHs in the study area. The results from the survey

TR030002-000442-ES Section 7 Marine sediment and water quality.pdf:31: undertaken for the proposed scheme are consistent with this data and have identified metal and PAH

NGCT_Final_ES at KK with figs.pdf:247: PAHs (Total) μg/kg 580 25000 11800 8600 21000 14867

NGCT_Final_ES at KK with figs.pdf:248: PAHs (Total) μg/kg 410 11000 4042

NGCT_Final_ES at KK with figs.pdf:251: 16. PAHs are of particular concern due to their persistence in the environment.

NGCT_Final_ES at KK with figs.pdf:251: therefore be concluded that levels of PAHs across the estuary, including a

NGCT_Final_ES at KK with figs.pdf:256: moderate levels of metals and generally elevated levels of PAHs, Lindane and

NGCT_Final_ES at KK with figs.pdf:298: the case for PAH contaminants as PAHs have a high affinity for sediments and

NGCT_Final_ES at KK with figs.pdf:326: however, recorded for individual PAHs, lindane and one sample for mercury.

IBPB8270R001F01_EIA REPORT(2).pdf:79: PAHs 0.1 None

IBPB8270R001F01_EIA REPORT(2).pdf:82:Concentrations of at least one PAH compound were present above Action Level 1 in samples recovered

IBPB8270R001F01_EIA REPORT(2).pdf:82:(and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

IBPB8270R001F01_EIA REPORT(2).pdf:83:Concentrations of PAH compounds within the Tees estuary have historically been elevated, and based on

IBPB8270R001F01_EIA REPORT(2).pdf:85:present for most metals, at most sample locations. The vast majority of PAH compounds were also present

IBPB8270R001F01_EIA REPORT(2).pdf:86:of PAH compounds.

IBPB8270R001F01_EIA REPORT(2).pdf:86:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

IBPB8270R001F01_EIA REPORT(2).pdf:86:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

IBPB8270R001F01_EIA REPORT(2).pdf:91:In terms of the PAHs, there are elevated concentrations above Action Level 1 in all samples recovered.

IBPB8270R001F01_EIA REPORT(2).pdf:91:of PAHs at similar levels. This indicates that elevated concentrations of PAHs are widespread throughout

IBPB8270R001F01_EIA REPORT(2).pdf:91:the Tees estuary and have been for a number of years. In addition, PAHs have a low water solubility and

IBPB8270R001F01_EIA REPORT(2).pdf:91:sediments and therefore remain bound. As a result, most PAHs will be strongly sorbed by particulate matter

IBPB8270R001F01_EIA REPORT(2).pdf:156:1, with the exception of PAHs which are elevated throughout the Tees estuary and have been for a

IBPB8270R001F01_EIA REPORT(2).pdf:298:exceedances of Action Level 1, with the exception of PAHs which are naturally elevated in the Tees), and

IBPB8270R001F01_EIA REPORT(2).pdf:413:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

IBPB8270R001F01_EIA REPORT(2).pdf:419:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

IBPB8270R001F01_EIA REPORT(2).pdf:421: • PAHs (USEPA 16);

IBPB8270R001F01_EIA REPORT(2).pdf:422: PAH (Total) 0.410 25.000 - - - -

IBPB8270R001F01_EIA REPORT(2).pdf:424:metals, PAH and PCBs above AL1. No elevations of AL2 were identified. Though showing signs of

IBPB8270R001F01_EIA REPORT(2).pdf:651: contaminants above Cefas Action contamination significantly above Action Level 1 (with the exception of PAHs which have

IBPB8270R001F01_EIA REPORT.pdf:79: PAHs 0.1 None

IBPB8270R001F01_EIA REPORT.pdf:82:Concentrations of at least one PAH compound were present above Action Level 1 in samples recovered

IBPB8270R001F01_EIA REPORT.pdf:82:(and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

IBPB8270R001F01_EIA REPORT.pdf:83:Concentrations of PAH compounds within the Tees estuary have historically been elevated, and based on

IBPB8270R001F01_EIA REPORT.pdf:85:present for most metals, at most sample locations. The vast majority of PAH compounds were also present

IBPB8270R001F01_EIA REPORT.pdf:86:of PAH compounds.

IBPB8270R001F01_EIA REPORT.pdf:86:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

IBPB8270R001F01_EIA REPORT.pdf:86:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

IBPB8270R001F01_EIA REPORT.pdf:91:In terms of the PAHs, there are elevated concentrations above Action Level 1 in all samples recovered.

IBPB8270R001F01_EIA REPORT.pdf:91:of PAHs at similar levels. This indicates that elevated concentrations of PAHs are widespread throughout

IBPB8270R001F01_EIA REPORT.pdf:91:the Tees estuary and have been for a number of years. In addition, PAHs have a low water solubility and

IBPB8270R001F01_EIA REPORT.pdf:91:sediments and therefore remain bound. As a result, most PAHs will be strongly sorbed by particulate matter

IBPB8270R001F01_EIA REPORT.pdf:156:1, with the exception of PAHs which are elevated throughout the Tees estuary and have been for a

IBPB8270R001F01_EIA REPORT.pdf:298:exceedances of Action Level 1, with the exception of PAHs which are naturally elevated in the Tees), and

IBPB8270R001F01_EIA REPORT.pdf:413:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

IBPB8270R001F01_EIA REPORT.pdf:419:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

IBPB8270R001F01_EIA REPORT.pdf:421: • PAHs (USEPA 16);

IBPB8270R001F01_EIA REPORT.pdf:422: PAH (Total) 0.410 25.000 - - - -

IBPB8270R001F01_EIA REPORT.pdf:424:metals, PAH and PCBs above AL1. No elevations of AL2 were identified. Though showing signs of

IBPB8270R001F01_EIA REPORT.pdf:651: contaminants above Cefas Action contamination significantly above Action Level 1 (with the exception of PAHs which have

MLA_2021_00215-APPLICATION-FORM.pdf:3:was had regarding the sediment analysis results and elevated levels of PAHs and heavy

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:4:Table 6 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:4:Table 7 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:24:were initially sent to Socotec to test for heavy metals, organotins, PAHs, PCBs, OCPs, TOC and PSA.

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:24:analysis undertaken by Socotec were received first. These indicated high concentrations of PAHs and

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:28: PAHs 0.1 None

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:30:4.2.2.4 PAHs

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:30:All sub-samples were analysed for the full suite of PAHs and the results are presented in Table 6 and Table

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:30:7. The majority of sub-samples were found to contain levels of PAHs above AL1. There is no AL2 for PAHs,

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:31:Table 6 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are highlighted yellow.

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:32:Table 7 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are highlighted yellow. (cont.)

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:33:The heavy metal and PAH analysis results indicate that the unconsolidated sediment within the dredge

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:79:contain heavy metals, PAHs and PCBs at levels exceeding AL1. Exceedances of AL2 were detected for

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:79:at the upper end of AL1 in one sub-sample. There is no AL2 for PAHs, however there are multiple sub-

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:85: 3.3. The recommend that Heavy metals (and Arsenic), Organotins, PAHs, PCBs, TOCs,

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:87:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:88:With regards to the PAH where levels are in exceedance of the action level sea disposal will not be

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:88:Mercury and Zinc in some samples. But looking at this purely from a PAH perspective you will

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:89:Attached are the sample analysis results from Socotec for heavy metals, tins, PAHs, PCBs and OCBs

MLA_2021_00215-PB5051-RHD-106-ZZ-RP-Z-0021 Tees Dock Ro-Ro 2 Environmental Report_Final-1.pdf:89:As you will see the reported PAH levels are higher than AL1 and in some cases significantly so. We

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:4:Table 6 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:4:Table 7 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:24:were initially sent to Socotec to test for heavy metals, organotins, PAHs, PCBs, OCPs, TOC and PSA.

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:24:analysis undertaken by Socotec were received first. These indicated high concentrations of PAHs and

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:28: PAHs 0.1 None

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:30:4.2.2.4 PAHs

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:30:All sub-samples were analysed for the full suite of PAHs and the results are presented in Table 6 and Table

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:30:7. The majority of sub-samples were found to contain levels of PAHs above AL1. There is no AL2 for PAHs,

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:31:Table 6 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are highlighted yellow.

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:32:Table 7 PAH contamination results (mg/kg) compared to Cefas ALs. Values exceeding AL1 are highlighted yellow. (cont.)

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:33:The heavy metal and PAH analysis results indicate that the unconsolidated sediment within the dredge

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:79:contain heavy metals, PAHs and PCBs at levels exceeding AL1. Exceedances of AL2 were detected for

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:79:at the upper end of AL1 in one sub-sample. There is no AL2 for PAHs, however there are multiple sub-

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:85: 3.3. The recommend that Heavy metals (and Arsenic), Organotins, PAHs, PCBs, TOCs,

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:87:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:88:With regards to the PAH where levels are in exceedance of the action level sea disposal will not be

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:88:Mercury and Zinc in some samples. But looking at this purely from a PAH perspective you will

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:89:Attached are the sample analysis results from Socotec for heavy metals, tins, PAHs, PCBs and OCBs

MLA_2021_00215-Tees Dock Ro-Ro 2 Environmental Report-13.pdf:89:As you will see the reported PAH levels are higher than AL1 and in some cases significantly so. We

Appendix 16.1a - DNV Report Rev1 2004.pdf:2:have been mapped for several metals (Ar, Cd, Cr, Cu, Hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging

Appendix 16.1a - DNV Report Rev1 2004.pdf:4:Appendix D PAH concentrations in sediments

Appendix 16.1a - DNV Report Rev1 2004.pdf:5:ecosystem. The exceptions are for the following PAHs: benzo(a)pyrene, Acenaphthylene,

Appendix 16.1a - DNV Report Rev1 2004.pdf:5:Anthracene and Benzo(a)anthracene. These PAHs are found in concentrations that exceeds the

Appendix 16.1a - DNV Report Rev1 2004.pdf:29:Cr, Cu, Hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging area 1 to 4. On Seals Sands the

Appendix 16.1a - DNV Report Rev1 2004.pdf:72:metals (Ar, Cd, Cr, Cu, hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging area 1 to 4 (see

Appendix 16.1a - DNV Report Rev1 2004.pdf:72:The sediment quality standards that have been used for metals, PCBs, PAHs and TBT are

Appendix 16.1a - DNV Report Rev1 2004.pdf:73:These PAHs are found in concentrations that exceeds the Probable Effect Level (PEL) according

Appendix 16.1a - DNV Report Rev1 2004.pdf:74:for PAHs in sediments according to the Canadian Environmental Quality Guidelines (/21/).

Appendix 16.1a - DNV Report Rev1 2004.pdf:81:Concentrations of several metals (Ar, Cd, Cr, Cu, hg, Ni, Pb and Zn), PCBs, PAHs and TBT in

Appendix 16.1a - DNV Report Rev1 2004.pdf:81:This means that there is a high probability of effects on the ecosystem due to the measured PAH

Appendix 16.1a - DNV Report Rev1 2004.pdf:81:contamination. For the above mentioned PAHs, levels above the risk limit have been observed in

Appendix 16.1a - DNV Report Rev1 2004.pdf:82:only specific areas have these high levels. Nor is it known if the levels of these PAHs also are

Appendix 16.1a - DNV Report Rev1 2004.pdf:82:contribute to the spreading of PAH contaminated sediments that have concentrations that exceed

Appendix 16.1a - DNV Report Rev1 2004.pdf:100: PAH CONCENTRATIONS IN SEDIMENTS

3 EIS Appendices (3).pdf:43: historical contaminants (heavy metals, pesticides, PCBs, TBT, PAHs) present

3 EIS Appendices (3).pdf:117:have been mapped for several metals (Ar, Cd, Cr, Cu, Hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging

3 EIS Appendices (3).pdf:119:Appendix D PAH concentrations in sediments

3 EIS Appendices (3).pdf:120:ecosystem. The exceptions are for the following PAHs: benzo(a)pyrene, Acenaphthylene,

3 EIS Appendices (3).pdf:120:Anthracene and Benzo(a)anthracene. These PAHs are found in concentrations that exceeds the

3 EIS Appendices (3).pdf:144:Cr, Cu, Hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging area 1 to 4. On Seals Sands the

3 EIS Appendices (3).pdf:187:metals (Ar, Cd, Cr, Cu, hg, Ni, Pb and Zn), PCBs, PAHs and TBT in dredging area 1 to 4 (see

3 EIS Appendices (3).pdf:187:The sediment quality standards that have been used for metals, PCBs, PAHs and TBT are

3 EIS Appendices (3).pdf:188:These PAHs are found in concentrations that exceeds the Probable Effect Level (PEL) according

3 EIS Appendices (3).pdf:189:for PAHs in sediments according to the Canadian Environmental Quality Guidelines (/21/).

3 EIS Appendices (3).pdf:196:Concentrations of several metals (Ar, Cd, Cr, Cu, hg, Ni, Pb and Zn), PCBs, PAHs and TBT in

3 EIS Appendices (3).pdf:196:This means that there is a high probability of effects on the ecosystem due to the measured PAH

3 EIS Appendices (3).pdf:196:contamination. For the above mentioned PAHs, levels above the risk limit have been observed in

3 EIS Appendices (3).pdf:197:only specific areas have these high levels. Nor is it known if the levels of these PAHs also are

3 EIS Appendices (3).pdf:197:contribute to the spreading of PAH contaminated sediments that have concentrations that exceed

3 EIS Appendices (3).pdf:215: PAH CONCENTRATIONS IN SEDIMENTS

Appendix 16.1b - DNV Addendum Report 2005.pdf:13:ecosystem. The exceptions are for the following PAHs: Acenaphthylene, Anthracene,

Appendix 16.1b - DNV Addendum Report 2005.pdf:13:the ecosystem due to the measured PAH contamination. These contaminants will most probably

20210729 MLA202000506 Tees South Bank - Further Proposed Sampling to delineate an exclusion zone+SJB.pdf:5: Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3:13. For the PAH results, in the absence of a defined Action Level 2, Cefas utilise the Gorham-Test

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3: low molecular weight (LMW) PAH analytes which are seen as acutely toxic, and a selection of

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3: the high molecular weight (HMW) PAH’s that are considered to be more long term acting (i.e.

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3: LMW PAHs and the total of the HMW PAHs are calculated and then compared to threshold

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3: values. If a total value (for either LMW or HMW selection of PAHs) does not exceed the effects-

20210406 MLA202000506 Tees South Bank Phase 1 Request to review interim analysis results SEAL Advice FINAL.pdf:3: and HMW PAHs, but only two samples exceeded the ERL for the HMW PAHs. This indicates

20210615 MLA202000506 MLA202000507 Tees South Bank Phases 1 and 2 - EIA _ SEAL Advice Followup+SJB.pdf:3: results for metals, organotins, PAHs and PCBs, my advice shall only comment on the PBDE

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:152:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:152:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:152:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:153:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:153:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:153:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:163:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:163:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:184:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:184:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:184: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:185: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:185: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf:535:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

MLA_2020_00506-MLA_2020_00506_2_RFI 19_Cefas Comments_MMO requested updates.pdf:1: note that PAHs are either consistent throughout the samples – the levels in glacial till and non-glacial/geological material are similar – or are

MLA_2020_00506-MLA_2020_00506_2_RFI 19_Cefas Comments_MMO requested updates.pdf:1: higher in the samples of glacial till. Ultimately, the PAH levels in these samples are not of concern (please refer to previous advice (Joe

MLA_2020_00506-MLA_2020_00506_2_RFI 19_Cefas Comments_MMO requested updates.pdf:1: sediment will not have been exposed to pollutants due to their transport pre-dating industrial activity. It could be the case that the PAH levels

MLA_2020_00506-MLA_2020_00506_2_RFI 19_Cefas Comments_MMO requested updates.pdf:1: observed reflect the background concentrations – as PAHs do occur naturally – but there is a lack of data to confirm or deny this. PBDEs, by

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:11:The results from BH34 show significant PAH concentrations throughout all depths, consistent with the metal

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:11:The concentration of PAH compounds in the geological mudstone were generally all below Action Level 1.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:13: • PAHs - benzo(a)pyrene, benzo(b)fluoranthene, benzo(g-h-i)perylene, benzo(k)fluoranthene and

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:17:there is a possibility that some PAH parameters could exceed their respective EQS during capital dredging.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:45:In summary, the assessment in Section 2 concluded that whilst there is a risk to EQS for several PAH

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:81: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:122: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:154: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:195: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:215: PAH Polycyclic Aromatic Hydrocarbons

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:256: Concentrations of THC and a suite of PAHs were analysed in sediments taken from several

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:256: depth ranges BRL. Concentrations of PAHs were compared with the Cefas action level AL1

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:312: run-off, atmospheric deposition (from combustion sources including PAHs) and natural

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:312: PAHs exceeding their respective Cefas AL1 threshold values.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf:321: PAHs exceeding their Cefas AL1 threshold value.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:163:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:163:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:185: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:185: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:535:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1137-MLA.2020.00506.2 South Bank Quay Marine Licence Variation 2 RFI 17-66.pdf:3:Further, no exceedances of Cefas Action Level 1 (AL1) thresholds for PAHs, THC or PCBs were recorded

MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1137-MLA.2020.00506.2 South Bank Quay Marine Licence Variation 2 RFI 17-66.pdf:7:Table A.2 Summary of PAH and THC sample analysis of material form the current capital dredge area

MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1137-MLA.2020.00506.2 South Bank Quay Marine Licence Variation 2 RFI 17-66.pdf:7: PAH / THC mg/kg dry weight

MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1137-MLA.2020.00506.2 South Bank Quay Marine Licence Variation 2 RFI 17-66.pdf:8: PAH / THC mg/kg dry weight

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:241: trace metals, organotins, PAHs, PCBs, organochlorines, and PBDEs. No

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:241: observed for metals, PAHs, PCBs, and organochlorines. There are no formal

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:243:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:244:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:245:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:from DBT24. Exceedances for DIV for total PAH (40mg/kg) were also recorded in samples collected from

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:Soil analysis recorded TPH at a maximum concentration of 285mg/kg (at 2B3 at 3.0m bgl) and PAH at

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:Groundwater analysis recorded a maximum concentration of TPH at 62µg/l in 2B3 and total PAH at less

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:273: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:273: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, slag (heavy metals and metalloids, sulphates and sulphides), PAHs,

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274:plant) (60 m south east of the site boundary, Metals, PAHs, asbestos, sulphates and sulphides.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Fuel and oil hydrocarbons, metals and metalloids, PAHs, sulphates and sulphides.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Heavy metals, sulphates/ sulphides, PAHs, fuel and oil hydrocarbons and phenols.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274:Dockyards including saw and timber mills Metals and metalloids, sulphates and sulphides, PAHs, fuel and oil hydrocarbons,

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:281:Benzole plant unsaturated Low Risk recorded exceedances for DIV for total PAH

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:11:The results from BH34 show significant PAH concentrations throughout all depths, consistent with the metal

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:11:The concentration of PAH compounds in the geological mudstone were generally all below Action Level 1.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:13: • PAHs - benzo(a)pyrene, benzo(b)fluoranthene, benzo(g-h-i)perylene, benzo(k)fluoranthene and

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:17:there is a possibility that some PAH parameters could exceed their respective EQS during capital dredging.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:45:In summary, the assessment in Section 2 concluded that whilst there is a risk to EQS for several PAH

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:81: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:122: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:154: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:195: Chrysene is known to coelute with Triphenylene and these peaks can not be resolved in the PAHSED UKAS accredited method. Chrysene and Triphenylene are resolved for MMO but this is

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:215: PAH Polycyclic Aromatic Hydrocarbons

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:256: Concentrations of THC and a suite of PAHs were analysed in sediments taken from several

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:256: depth ranges BRL. Concentrations of PAHs were compared with the Cefas action level AL1

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:312: run-off, atmospheric deposition (from combustion sources including PAHs) and natural

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:312: PAHs exceeding their respective Cefas AL1 threshold values.

MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf:321: PAHs exceeding their Cefas AL1 threshold value.

R-2022-0816-FFM-10035117-AUK-XX-XX-CO-ZZ-0582-01-PR GI Memo_Part1(1).pdf:3: Speciated PAH

R-2022-0816-FFM-10035117-AUK-XX-XX-CO-ZZ-0582-01-PR GI Memo_Part1(1).pdf:4: Speciated PAH

R-2022-0515-CD-L05858-CLK-XX-XX-RP-GT-0005 P01.pdf:25: PAH

R-2022-0515-CD-L05858-CLK-XX-XX-RP-GT-0005 P01.pdf:25: Total PAH 100 use

Environmental Statement, Chapter H Ground Conditions and Remediation Section 6 Mitigation.pdf:4: PAHs) determinands and there is therefore a requirement for its collection and treatment prior

R-2021-0422-CD-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.PDF:13: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2021-0422-CD-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.PDF:15:benzene, dibenzofuran, and PAHs that were measured in excess of the Generic Assessment Criteria

R-2021-0422-CD-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.PDF:22: from materials impacted with Lead, arsenic, asbestos, cyanide, and PAHs; and,

R-2021-0422-CD-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.PDF:41:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:650: PAH Glass 20g EPA Victoria 14 days -

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:651: PAH Glass 500 ISO 5667 3:2018 none 4 days

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: Soils and associated materials are extracted in dichloromethane (DCM) using sonication. The PAH concentration

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: is recorded both as “Total PAH” and as “Speciated PAH”, specified in terms of the 16 US EPA “Priority In-house method based on US EPA Method 8100, Polynuclear Aromatic

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: DETSC 3301 PAH in Soil by GC-FID UKAS (16 PAH's only)

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: 1.6 mg/kg Total PAH

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: Soils are extracted into hexane: acetone by shaking. The PAH concentration is recorded both as “Total PAH” and

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: as “Speciated PAH”, specified in terms of the 16 US EPA “Priority Pollutant” Polycyclic Aromatic In-house method based on US EPA Method 8100, Polynuclear Aromatic

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: DETSC 3302 Hexane / Acetone Extracted PAH in Soil by GC-FID Not Accredited

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: 1.6 mg/kg Total PAH

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: The PAHs in the soil sample are extracted into hexane: acetone by shaking. The PAHs in the extract are separated UKAS (All 16 PAH's)

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: by gas chromatography and identified by the mass selective detector. The concentration of each PAH is

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: (GC/MS) 0.10 mg/kg Total PAH

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: The PAHs in the water sample are extracted into dichloromethane by shaking. The PAHs in the extract are Semivolatile Organic Compounds by Gas Chromatography – Mass Spectrometry

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: separated by gas chromatography and identified by the mass selective detector. The concentration of each PAH is (GC/MS).

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:663: DETSC 3304 Polyaromatic Hydrocarbons in Waters by GC-MS 10 ng/l each UKAS (16 PAH's only)

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:672:Sum PAH (USEPA 16) 0.1 mg/kg na 700.00 110.00 700.00

R-2022-0342-CD-10035117-AUK-XX-XX-RP-ZZ-0395-03-GE Plot.pdf:676:Sum PAH (USEPA 16) 0.1 mg/kg na 700.00 110.00 700.00

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:7: PAHs 0.00025 Annual - AQS Objective

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:12: the Middlesbrough AURN site. For the assessment of baseline concentrations of PAHs, only

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:12: monitored concentrations of benzo-a-pyrene (BaP) have been considered as this is the only PAH

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:18: PaHs 0.18 ng/m³ Maximum background concentration

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:37: PAHs Annual mean pg/m³ 250 180 4.23 3.85 3.64 3.69 3.42 4.23 1.69% 184.23 73.69%

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:39: • Annual mean PAHs;

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: 7.2.5 Annual mean PAHs

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: The annual mean PAHs (as BaP) PC from the Proposed ERF is predicted to be 1.67% of the AQAL at

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: Table 35 shows the annual mean PAH PC at the identified sensitive human receptor locations. PCs

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: Table 35: Annual Mean PAHs (as BaP) Impact at Identified Sensitive Receptors

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:81: Annual Mean PAHs (as

R-2023-0246-RMM-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:81: Figure 13 - Annual Mean PAHs

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:22:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:22:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf:14:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

R-2020-0685-ESM-Appendix 6_Sediment sampling plan.pdf:4: trace metals, organotins, PAHs, PCBs, organochlorines, and PBDEs. No

R-2020-0685-ESM-Appendix 6_Sediment sampling plan.pdf:4: observed for metals, PAHs, PCBs, and organochlorines. There are no formal

R-2020-0685-ESM-Appendix 6_Sediment sampling plan.pdf:6:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0685-ESM-Appendix 6_Sediment sampling plan.pdf:7:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0685-ESM-Appendix 6_Sediment sampling plan.pdf:8:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:17: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:17: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:from DBT24. Exceedances for DIV for total PAH (40mg/kg) were also recorded in samples collected from

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:Soil analysis recorded TPH at a maximum concentration of 285mg/kg (at 2B3 at 3.0m bgl) and PAH at

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:Groundwater analysis recorded a maximum concentration of TPH at 62µg/l in 2B3 and total PAH at less

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:27: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:27: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, slag (heavy metals and metalloids, sulphates and sulphides), PAHs,

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28:plant) (60 m south east of the site boundary, Metals, PAHs, asbestos, sulphates and sulphides.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Fuel and oil hydrocarbons, metals and metalloids, PAHs, sulphates and sulphides.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Heavy metals, sulphates/ sulphides, PAHs, fuel and oil hydrocarbons and phenols.

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28:Dockyards including saw and timber mills Metals and metalloids, sulphates and sulphides, PAHs, fuel and oil hydrocarbons,

R-2020-0685-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:35:Benzole plant unsaturated Low Risk recorded exceedances for DIV for total PAH

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:7: PAHS.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:24:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:24: PAHs, phenol and TPH. Were taken from within the site boundary

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:24: sulphate cyanide and PAHs, phenol and TPH

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:25: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:25: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:39:  Railway ballast containing metals and PAHs,

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:39: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:40: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:40: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:41: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:41: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:42: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:42: exception of PAH results.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:42: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:42: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:43: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:54: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:54: westerly direction (towards the Tees). The pH was alkaline. TPH and PAHs were below detection, but copper

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:55: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:55: westerly direction (towards the Tees) The pH was alkaline. TPH and PAHs were below detection limits, but

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:75: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:75:  PAHs – 1 sample (GAC 40mg/kg)

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:85: hydrocarbons, PAHs and BT

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:90:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s, VOCs, SVOCs and aromatic

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P02.pdf:90:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:7: PAHS.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:22:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:22: PAHs, phenol and TPH. Were taken from within the site boundary

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:22: sulphate cyanide and PAHs, phenol and TPH

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:23: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:23: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:37:  Railway ballast containing metals and PAHs,

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:37: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:38: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:38: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:39: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:39: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:40: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:40: exception of PAH results.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:40: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:40: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:41: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:52: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:52: westerly direction (towards the Tees). The pH was alkaline. TPH and PAHs were below detection, but copper

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:53: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs.

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:53: westerly direction (towards the Tees) The pH was alkaline. TPH and PAHs were below detection limits but copper

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:73: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:73:  PAHs – 1 sample (GAC 40mg/kg)

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:83: hydrocarbons, PAHs and BT

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:88:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s, VOCs, SVOCs and aromatic

R-2019-0427-FFM-41825-WOOD-XX-XX-RP-OC-0002_A_P01.pdf:88:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2021-0166-FFM-Environmental Risk Assessment.pdf:23:TPB28 1.5m (the concentration was 11x EQS). The same five PAHs were detected above DWS in Area B,

R-2021-0166-FFM-Environmental Risk Assessment.pdf:25:in Area A exceeded WQS screening criteria for copper and manganese, and several PAH compounds.

R-2021-0166-FFM-Environmental Risk Assessment.pdf:25:sediment suspension as samples were filtered on the second monitoring round. The TPH and PAH

R-2021-0166-FFM-Environmental Risk Assessment.pdf:29:Several PAH compounds do not have WQS, but these will be adequately covered under recommendations for

R-2021-0166-FFM-Environmental Risk Assessment.pdf:29:the PAH compounds identified as exceeding their applicable WQS. PAH compounds are generally of low

R-2021-0166-FFM-Environmental Risk Assessment.pdf:29:Low levels of dissolved petroleum hydrocarbons, including PAHs have been detected in shallow groundwater

R-2021-0166-FFM-Environmental Risk Assessment.pdf:58: PAHs

R-2021-0166-FFM-Environmental Risk Assessment.pdf:58: PAH - USEPA 16, Total 0.1 mg/kg None 330 71

R-2021-0166-FFM-Environmental Risk Assessment.pdf:64: PAHs

R-2021-0166-FFM-Environmental Risk Assessment.pdf:64: PAH Total 0.04 ug/l 85 0.61

R-2021-0166-FFM-Environmental Risk Assessment.pdf:67: PAH Total na

R-2021-0166-FFM-Environmental Risk Assessment.pdf:69: PAHs

R-2021-0166-FFM-Environmental Risk Assessment.pdf:69: PAH Total 0.04 ug/l 4.5 100

R-2022-0494-FFM-21089271_1.pdf:13: Railways and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2022-0494-FFM-21089271_1.pdf:13: Metals, TPH, PAHs, VOC, SVOC,

R-2022-0494-FFM-21089271_1.pdf:13: Former Iron Works, Slag Brick Works, Slag asbestos, TPH, PAH, cyanides,

R-2022-0494-FFM-21089271_1.pdf:13: 35m west (stretching onto Metals, asbestos, TPH, PAH, VOC,

R-2022-0494-FFM-21089271_1.pdf:13: Made Ground including slag – used for filling Surrounding site to north, PAHs, TPH, cyanide, thiocyanate,

R-2022-0494-FFM-21089271_1.pdf:14:material composition (e.g., metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2022-0494-FFM-21089271_1.pdf:14:Concentrations of PAH were measured in 24 of the 27 Made Ground samples with a maximum total PAH

R-2022-0494-FFM-21089271_1.pdf:14:of waste). This is considered to be an outlier with the average total PAH concentration being 46.5mg/kg.

R-2022-0494-FFM-21089271_1.pdf:14:Typically made ground samples assessed contained PAH compounds with no significant difference noted

R-2022-0494-FFM-21089271_1.pdf:15:horizon at 4.70m bgl and reported lower concentrations of TPH and PAH.

R-2022-0494-FFM-21089271_1.pdf:110:CE087 PAH (total of USEPA 16) Solvent extraction, GC-MS As received 0.34 mg/kg

R-2022-0494-FFM-21089271_1.pdf:114:CE051 PAH (total of USEPA 16) Solvent extraction, GC-MS 1.6 µg/l

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:5: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:5: tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:6: SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:17:benzene, dibenzofuran, 1,2 dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:19:metals, inorganics and PAH. This was not unexpected given that some of the sentinel wells were installed

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:23:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:23:(including tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:24:Contaminants associated with the above include metals, asbestos, hydrocarbons (including tars), PAH,

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:24:potential to affect groundwater quality include metals, hydrocarbons, PAH, inorganics including cyanide,

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:24:contaminants with the potential to affect groundwater quality include metals, TPH, PAH, VOC and SVOC.

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:Similarly to metals, PAH and TPH are found throughout the site and are also likely to be associated with the

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:For PAH, the highest sum PAH concentration was measured in SBA_AUK_TP154 at 0.6m (99,000mg/kg),

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:coinciding with the highest sum TPH concentrations in the northeast of SBA. The next highest sum PAH

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:2,700mg/kg respectively). Similarly to TPH, further lower sum PAH concentrations were located across the

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:26:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:27:Total PAH was measured above the laboratory MDL in all 52 monitored locations. Again, the highest

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:27:The sentinel wells which measured the highest total PAH concentrations were BH2010 (maximum 220µg/l)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:29:of metals and inorganics were measured above the MDL, along with a number of PAH compounds. Measured

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:33: Hydrocarbons (including PAH, TPH and BTEX)

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:40:site, exceed the SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate,

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:41:undertaken) for several of the wells where TPH or PAH concentrations exceed and may indicate entrainment

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:82:Pyrene µg/L ~ 163 203 190 0.82 ~ Yes1 (representing one of the more mobile PAH), fluoranthene, anthracene and

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:82:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:83: petroleum hydrocarbons, PAH and indicators included within the assessment are

R-2021-0855-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02_SB_DQRA_Part1.pdf:83:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0205-SC-Bran Sands EIA Screening Request_FINAL reduced signed.pdf:43: contaminants 21 particularly heavy metals and PAHs 22. Data from the YPP and previous

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:25:  Former Pellet Plant Metals, asbestos, TPH, PAH, VOC, SVOC, cyanide,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:25: Railway lines and sidings Metals, asbestos, TPH, PAH, sulphate, sulphide, and pH

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:26: Metals, asbestos, TPH, PAH, VOCs, SVOCs, chloride,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:26:  Biproducts Plant Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:26: Metals, TPH, PAH, VOCs, SVOCs, chloride, ammonia,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:26:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29:Concentrations of PAH were measured in the almost all the samples of slag dominant material and granular

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29:and wood had been identified in the trial pits; samples from these locations showed levels of PAH notably

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29:Leached concentrations of PAH were measured all three samples tested and comprised a broad range of light

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: concentrations of PAH within the same samples were low. A black clayey material was noted in S1-

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: TPH and 19 µg/l PAH was measured in groundwater from monitoring well S1-BH12 which is screened

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: concentration of 330mg/kg PAH was measured in S1-TPH23 (3.4m bgl), located in the centre of Zone

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: hydrocarbons in the C16-C35 range in S1-TPH24 and middle molecular weight PAH in S1-TPH23. A

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29: concentration of 8.8µg/l TPH and 2.9µg/l PAH were measured in groundwater from monitoring well

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:29:  An elevated concentration of TPH and PAH (25,000mg/kg and 230mg/kg respectively) was measured

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: northern corner of the RCO area, the concentration of PAH within the same sample was 570mg/kg. A

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: 120µg/l TPH and 130µg/l PAH was measured following leaching tests on the sample, the PAH

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: north-east of SSI2, concentrations of PAH within the same samples were low in comparison to the

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: to the main workshops and stores. An elevated concentration of PAH (150mg/kg) was also in a sample

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30: south eastern boundary of SSI2, the concentration of PAH within the same sample was 670mg/kg. A

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30:In addition, a sample from S2-TPA29 (4.9m bgl) was reported by CH2M to contain a PAH concentration of

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:30:The locations of elevated TPH and PAH are shown on Figure 13 below and in Appendix C.

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:37: dominant Made Ground, and the highest concentrations of PAH in granular Made Ground

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:37:  Tests identified that metals readily leached from Made Ground deposits, TPH and PAH were also

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:37: noted to leach in some samples. Metals, TPH and PAH were also detected in groundwater.

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:64: Likely to be several metres thick due PAHs, asbestos,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:64: plant area PAHs, phenols,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:67: observations PAHs

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:70: as a result of spillages / loss of sulphates and PAHs.

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:72: PAOC from coke manufacture. Structures TPH, PAH, ammonia,

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:75: PAH - USEPA 16, Total 138 137 670 0.05 14.293 59.377

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:76: Total PAH 106 86 570 0.05 11.487 60.331

R-2021-1048-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI1_SSI2A_GI_SCR.pdf:77: Total PAH 9 9 330 0.05 40.760 102.641

R-2021-1048-FFM-Officer Report 1048.pdf:8:based on an active SPR linkage including Asbestos, PAH and NAPL with

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:3: Theoretical risk to the aquifer (inorganics, metals, PAH

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:185: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual REPORT SSI 2.pdf:185: (730 days), PAH MS (14 days), PCB (30 days), pH +

R-2021-1048-FFM-Earthworks Specification.pdf:23: PAH • Boron (w sol) and Free) excavation base • One sample per 100x100m extent of

R-2021-1048-FFM-Earthworks Specification.pdf:31: PAHs

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: GRO,BTEX, Phenols, PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: CH2M-SSI1 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: CH2M – SSI2 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: Within SSI Landholdings Sulphate, Chloride TPH, BTEX, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22: Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:23:criteria adopted, with localised exceedances for PAH, lead and zinc.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:25: sulphate, TPH including tar, BTEX, phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:25: Asbestos, TPH and tars, BTEX, phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:26: Asbestos, hydrocarbons, ash, PAH, phenol, sulphates,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:26: Substations Asbestos, hydrocarbons, PAH, PCBs

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-03-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:26: Material Storage - Coal/coke breeze, ore, pellet, and PAH and metals

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:26: Phenols, PAH, VOC, SVOC,, nitrogen compounds

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

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:7:EPA16 16 priority PAHs as identified by the USA’s Environmental Protection Agency

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:8:of PAH contained within the Coke Oven Gas Main which also applies to SSI1.

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:24: 29/06/2016. of PAH on site, contained within the

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:27:and PAHs. These are often localised as a result of spillages, but the occurrence and extent of this was

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:29: • PAH Total EPA16 (40mg/kg)

R-2021-1048-FFM-SSI 1 Desk Study_final(2).pdf:38: nitrogen and contains condensed PAHs. coke oven gas main. All works to be a safe

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:11: bitumen and PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:11: casting, tars, PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:13: macadam works and slag wool works immediately east, with Those above plus TPH, PAH and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: GRO,BTEX, Phenols, PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: CH2M-SSI1 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: CH2M – SSI2 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: Within SSI Landholdings Sulphate, Chloride TPH, BTEX, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:21: Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:22:criteria adopted, with localised exceedances for PAH, lead and zinc.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:24: Former industrial uses - iron and steel making plant Phenols, PAH, VOC, SVOC, PCB

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:24: Asbestos, TPH, BTEX, Phenols, PAH, VOC, SVOC

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:24: Railways Asbestos, hydrocarbons, ash, PAH, phenol, sulphates

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment(2).pdf:24: Phenols, PAH, VOC, SVOC, PCB, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:16:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:17:Levels of PAH were measured above the screening criteria in three locations, the SPL linkage for these

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:24: from materials impacted with asbestos, and PAHs; and,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-02-Rem_Strat_NetZero.pdf:40:Metals, asbestos, TPH including tars, PAH, cyanides,

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: for the Site, with the risks from asbestos and PAH mitigated by the requirement to import a

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:5: included metals, hydrocarbons including PAH and TPH, inorganics including cyanide,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:7: pathways in relation to asbestos (identified in shallow soils) and PAH (identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:33:buildings or another suitable cover system. The depth at which the PAH exceedances were identified in

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:34:concentration of 1.2mg/kg. The SVOC 2-methylnaphthalene is a type of PAH, with detections of this compound

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:34:corresponding with samples in which the remaining PAH analysed were also measured. The remaining PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:35:A sample from S2-TPA83 at 3m bgl exceeded the GAC for two PAH compounds, which were considered to be

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:35:development. The depth at which PAH were measured in S1-BH13A is such that these pathways are not

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:41:Additional analysis has been undertaken to test for PAHs with a suitable MDL however the results of this are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:41:of PAH (including eight compounds within the PAH suite and additionally carbazole, dibenzofuran, 2-

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:42:TPH and PAH is required. It is noted that while certain metals are not considered to require further evaluation

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:detailed assessment. In addition, potentially active pollutant linkages have been identified in relation to PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:43:areas, which will act as a suitable cover system to break the linkages driving risk in relation to PAH and asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:44:selected metals and inorganics TPH and PAH is required.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:45:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:45:Contaminants associated with the above include metals, hydrocarbons (including tars), PAH, inorganics

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:46:well as potentially present as a result of anthropogenic sources. This includes metals, PAH (which could be

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:46:Associated contaminants with the potential to affect groundwater quality include metals, hydrocarbons, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:Similarly to metals, PAH and TPH are found throughout the Site. Generally, no discernible correlation with

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:albeit on the whole, the measured concentrations of TPH and PAH are likely to be associated with the imported

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:The highest concentrations of sum PAH in the hundreds of mg/kg were measured in S1-BH13A, located in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:S2-TPA83, and as such, the PAH are likely to be associated with the presence of tar.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:47:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:analysed). The highest concentrations of sum PAH were associated with groundwater samples collected from

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:monitoring wells screening Made Ground (maximum concentration of sum PAH of 92µg/l), with maximum

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:measured concentrations of sum PAH concentrations in monitoring wells screening the superficial deposits and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:Review of the lateral distribution indicates that concentrations of sum PAH were typically identified in the ones

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:surface material. Concentrations of sum PAH in the northern portion of the Site were typically less than 1µg/l.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:While it appears evident that elevated PAH in the south of the Site are likely associated with the historical land

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:manganese, TPH and PAH. Iron and manganese were identified in soils across the Site, albeit were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:stocking area). TPH and PAH have also been measured in soils across the Site, again, likely due the Made

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:51:Ground. However, isolated elevated concentrations of TPH and PAH have also been identified, which may

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:52:• PAH, which were identified across the Site, albeit the highest concentrations were typically identified in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:56:“For contaminants which are characterised by a high partition coefficient (e.g. some PAH compounds), the rates

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:59:analysis has been undertaken to test for PAHs with a lower MDL however the results of this are not available at

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:59:of this report on the basis that the risk from PAHs has been further evaluated below given that concentrations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:59:of PAH in excess of the SSAC at 50m have been identified in the remaining data.

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:796: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:797: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:798: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:799: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:800: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:801: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:802: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:803: Geology TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:806: days), PAH MS (14 days), PCB (30 days), pH + Conductivity (7

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:806: days), PAH MS (14 days), pH + Conductivity (7 days),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:807: days), PAH MS (14 days), pH + Conductivity (7 days),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:807: days), PAH FID (14 days), pH + Conductivity (7 days),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:807: PAH FID

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:807: days), PAH FID (14 days), pH + Conductivity (7 days),

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:808: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:810: PAH 16 Total mg/kg <16 <16 <22 <41 <16 <120 <50 <16 <16 <100 <16 <16 <17 <56 <16 <16 <16 <22 <16 <309 <26 <18 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16 <16 <16 <16 <16 <18 <47 <16 <16 <16 <26 <16 <16 <16 <16 <16 <153 <16 <16 <16 <68 - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:810: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3 <0.1 <0.1 <0.1 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1 <0.1 0.3 1.8 <0.1 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1 <0.1 - - - <0.1 <0.1 0.26 <0.1 6.3 0.17 <0.1 <0.1 4 <0.1 3 - <0.1 <0.1 - <0.1 <0.1 <0.1 3.1 <0.1 <0.1 <0.1 - 7 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:811: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - 0.15 4.4 4.3 0.37 25 2.3 0.31 4.2 2.2 1.1 3.4 9.8 0.12 1.6 0.71 0.05 3.6 0.35 1.1 0.67 - 1.8 - 0.63 - - 0.18 16 0.05 4.5 - 1.1 - 1.4 29 3.9 0.57 0.8 33 0.8 0.8 21 0.8 0.8 0.8 - 38 1.8 330 29 0.8 13 8.6 21 1.5 0.26 1.1 7.3 0.74 14 0.05 - - 34 1.1 - 30 6 0.05 8.2 3.2 1.6 0.57 0.61 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:811: PAHs (Sum of total) mg/kg 0.22 0.16 <0.1 - 2.1 0.56 9.3 - 0.33 <0.1 - - - - - - - - - - <0.1 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32 2.5 <14.91 2.9 0.44 0.44 <0.1 2.5 <0.1 <0.1 - 5.8 2.6 <0.1 - 7 0.4 - 31 <0.1 0.53 - 8.1 0.8 - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:812: PAH 16 Total mg/kg 38 1.8 5 0.05 9.6 4.1 - 0.34 0.05 2.4 0.53 3.2 - 0.05 - 0.05 0.67 - - 7.7 1.5 - - - - 1.6 - - - - - - - 0.99 10 7.7 1.2 0.75 0.05 - 0.49 0.16 15.94 0.05 1.8 0.05 2.7 2.5 2.1 0.05 1.1 0.05 - 0.55 0.56 0.05 0.05 1.1 4.1 - 0.2 11 0.05 1.1 0.05 10 1.4 6.4 0.05 38 150 44 0.21 0.15 38 670 43 27 - 0.05 1.8 0.05 6.8 0.21 0.05 1.7 1.2 0.05 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:812: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - 1.3 <0.1 - - - 5.8 - 1.6 - - 1.9 0.91 97 - 3.9 - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - 0.49

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:821: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:822: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:823: PAHs (Sum of total) µg/L - - 15 - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:824: PAH 16 Total µg/L <160 <160 <160 - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:824: PAHs (Sum of total) µg/L - - - 0.61 <0.2 - <0.2 0.63 0.28 - - 0.39 <0.2 - - - - 0.38 0.36 - - 0.52 - - 0.23 - - - 0.22 0.5 - 0.21 0.76 - - - - 0.39 0.2 - - - - 6.8 - - 5.6 1.5 - - 0.42 - - 2.9 9.6 5.3 0.22 0.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:826: Volatile Organic Compounds, asbestos and Polychlorinated Biphenyls data was analysed from 2017 onwards. It is noted that while the 2004 Enviros investigation included speciated PAH analysis, only the sum PAH analytical testing data from this

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:826: investigation is presented here (51No. samples analysed for speciated PAH). This is due to the nature of the data provided for review; as such, while the measured concentrations have been included in the consideration of the human health risk assessment

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:826: for the individual PAH fractions, they have not been included in this screening table.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:828:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:829:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:831:6 The compounds detected are PAH, with a review of the distribution of the remaining PAH for which criteria were available for comparison indicating that they were typically identified in the same location and at similar concentrations. As such, the remaining PAH for which WQS are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:831:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:831: Yes(i) Compound considered to be associated with Polycylic Aromatic Hydrocarbon, with the exception of free cyanide. As such, these compounds have been assessed further indirectly through indicator compounds (either PAH or total cyanide), in the absence of readily available WQS for

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:834:#10:Water Supply (Water Quality) Regulations 2016. Value of 0.1µg/l for PAH split between four individual PAH. Requires summation

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:836: PAHs (Sum of total) µg/L 2 1 15 - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:836:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-02-LWoW_DQRA.pdf:842: contamination was identified (samples containing sum PAH greater than 1mg/kg were excluded). The SOM was converted

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:832: Naphthalene (14 days), PAH MS (14 days), pH +

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:941: days), PAH MS (14 days), pH +

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:943: days), PAH MS (14 days), pH +

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:973: PAH is extracted from one litre of filtered water sample by

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:973: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:973: Note for PAH by SPE

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: dichloromethane (DCM) using sonication. The PAH

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: concentration is recorded both as “Total PAH” and as

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: PAH concentration is recorded both as “Total PAH” and

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:992: 3302 1.6 mg/kg Total PAH

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: The PAHs in the soil sample are extracted into hexane:

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:993: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:1004: PAH Glass 20g EPA Victoria 14 days -

R-2021-1048-FFM-4153 & 4154 Area A Former Steelworks Redcar Contract 1 & 2 (Area A) (Final report).pdf:1005: PAH Glass 500 CIP 2 Tech Spec none 5 days

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1258: PAHs

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1267: PAHs

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1276: PAHs

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1286: PAHs

R-2021-1048-FFM-4339 Preliminary Onshore GI for NZT (Draft Report).pdf:1295: PAHs

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: for the Site, with the risks from asbestos and PAH mitigated by the requirement to import a

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:5: included metals, hydrocarbons including PAH and TPH, inorganics including cyanide,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:7: pathways in relation to asbestos (identified in shallow soils) and PAH (identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:35:buildings or another suitable cover system. The depth at which the PAH exceedances were identified in

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:36:concentration of 1.2mg/kg. The SVOC 2-methylnaphthalene is a type of PAH, with detections of this compound

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:36:corresponding with samples in which the remaining PAH analysed were also measured. The remaining PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:37:A sample from S2-TPA83 at 3m bgl exceeded the GAC for two PAH compounds, which were considered to be

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:37:development. The depth at which PAH were measured in S1-BH13A is such that these pathways are not

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:44:Additional analysis has been undertaken to test for PAHs with a suitable MDL however the results of this are

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:44:of PAH (including eight compounds within the PAH suite and additionally carbazole, dibenzofuran, 2-

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:44:TPH and PAH is required. It is noted that while certain metals are not considered to require further evaluation

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:detailed assessment. In addition, potentially active pollutant linkages have been identified in relation to PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:45:areas, which will act as a suitable cover system to break the linkages driving risk in relation to PAH and asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:46:selected metals and inorganics TPH and PAH is required.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:47:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:47:Contaminants associated with the above include metals, hydrocarbons (including tars), PAH, inorganics

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:48:well as potentially present as a result of anthropogenic sources. This includes metals, PAH (which could be

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:48:Associated contaminants with the potential to affect groundwater quality include metals, hydrocarbons, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:Similarly to metals, PAH and TPH are found throughout the Site. Generally, no discernible correlation with

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:albeit on the whole, the measured concentrations of TPH and PAH are likely to be associated with the imported

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:The highest concentrations of sum PAH in the hundreds of mg/kg were measured in S1-BH13A, located in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:S2-TPA83, and as such, the PAH are likely to be associated with the presence of tar.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:49:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:analysed). The highest concentrations of sum PAH were associated with groundwater samples collected from

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:monitoring wells screening Made Ground (maximum concentration of sum PAH of 92µg/l), with maximum

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:measured concentrations of sum PAH concentrations in monitoring wells screening the superficial deposits and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:Review of the lateral distribution indicates that concentrations of sum PAH were typically identified in the ones

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:surface material. Concentrations of sum PAH in the northern portion of the Site were typically less than 1µg/l.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:While it appears evident that elevated PAH in the south of the Site are likely associated with the historical land

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:manganese, TPH and PAH. Iron and manganese were identified in soils across the Site, albeit were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:stocking area). TPH and PAH have also been measured in soils across the Site, again, likely due the Made

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:53:Ground. However, isolated elevated concentrations of TPH and PAH have also been identified, which may

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:54: PAH, which were identified across the Site, albeit the highest concentrations were typically identified in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:58:“For contaminants which are characterised by a high partition coefficient (e.g. some PAH compounds), the rates

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:61:analysis has been undertaken to test for PAHs with a lower MDL however the results of this are not available at

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:61:of this report on the basis that the risk from PAHs has been further evaluated below given that concentrations

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:61:of PAH in excess of the SSAC at 50m have been identified in the remaining data.

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:803: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:804: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:805: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:806: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:807: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:808: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:809: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:810: Geology TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:813: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:814: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:814: PAH FID

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:814: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:815: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:818: PAH 16 Total mg/kg <16 <16 <22 <41 <16 <120 <50 <16 <16 <100 <16 <16 <17 <56 <16 <16

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:818: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:823: PAH 16 Total mg/kg <16 <22 <16 <309 <26 <18 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16 <16 <16

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:823: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:828: PAH 16 Total mg/kg <16 <16 <18 <47 <16 <16 <16 <26 <16 <16 <16 <16 <16 <153 <16 <16 <16 <68

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:828: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:833: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:833: PAHs (Sum of total) mg/kg 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3 <0.1 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:838: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:838: PAHs (Sum of total) mg/kg <0.1 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1 <0.1 0.3 1.8 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:843: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:843: PAHs (Sum of total) mg/kg 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1 <0.1 - - - <0.1 <0.1 0.26 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:848: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:848: PAHs (Sum of total) mg/kg 6.3 0.17 <0.1 <0.1 4 <0.1 3 - <0.1 <0.1 - <0.1 <0.1 <0.1 3.1 <0.1 <0.1 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:853: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:853: PAHs (Sum of total) mg/kg - 7 - 0.22 0.16 <0.1 - 2.1 0.56 9.3 - 0.33 <0.1 - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:858: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:858: PAHs (Sum of total) mg/kg - - - - - <0.1 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32 2.5 <14.91 2.9

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:863: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:863: PAHs (Sum of total) mg/kg 0.44 0.44 <0.1 2.5 <0.1 <0.1 - 5.8 2.6 <0.1 - 7 0.4 - 31 <0.1 0.53 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:868: PAH 16 Total mg/kg - - 0.15 4.4 4.3 0.37 25 2.3 0.31 4.2 2.2 1.1 3.4 9.8 0.12 1.6 0.71 0.05

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:868: PAHs (Sum of total) mg/kg 8.1 0.8 - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:873: PAH 16 Total mg/kg 3.6 0.35 1.1 0.67 - 1.8 - 0.63 - - 0.18 16 0.05 4.5 - 1.1 - 1.4

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:873: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:878: PAH 16 Total mg/kg 29 3.9 0.57 0.8 33 0.8 0.8 21 0.8 0.8 0.8 - 38 1.8 330 29 0.8 13

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:878: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:883: PAH 16 Total mg/kg 8.6 21 1.5 0.26 1.1 7.3 0.74 14 0.05 - - 34 1.1 - 30 6 0.05 8.2

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:883: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:888: PAH 16 Total mg/kg 3.2 1.6 0.57 0.61 - 38 1.8 5 0.05 9.6 4.1 - 0.34 0.05 2.4 0.53 3.2 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:888: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:893: PAH 16 Total mg/kg 0.05 - 0.05 0.67 - - 7.7 1.5 - - - - 1.6 - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:893: PAHs (Sum of total) mg/kg - - - - 1.3 <0.1 - - - 5.8 - 1.6 - - 1.9 0.91 97 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:898: PAH 16 Total mg/kg - - 0.99 10 7.7 1.2 0.75 0.05 - 0.49 0.16 15.94 0.05 1.8 0.05 2.7 2.5 2.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:898: PAHs (Sum of total) mg/kg 3.9 - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:903: PAH 16 Total mg/kg 0.05 1.1 0.05 - 0.55 0.56 0.05 0.05 1.1 4.1 - 0.2 11 0.05 1.1 0.05 10 1.4

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:903: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:908: PAH 16 Total mg/kg 6.4 0.05 38 150 44 0.21 0.15 38 670 43 27 - 0.05 1.8 0.05 6.8 0.21 0.05

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:908: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:913: PAH 16 Total mg/kg 1.7 1.2 0.05 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:913: PAHs (Sum of total) mg/kg - - - 0.49

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:925: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:926: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:927: PAHs (Sum of total) µg/L - - - - - - - - - - 15 - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:928: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - <0.2

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:930: PAH 16 Total µg/L <160 <160 <160 - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:930: PAHs (Sum of total) µg/L - - - 0.61 <0.2 - <0.2 0.63 0.28 - - 0.39 <0.2 - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:935: PAH 16 Total µg/L - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:935: PAHs (Sum of total) µg/L 0.38 0.36 - - 0.52 - - 0.23 - - - 0.22 0.5 -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:940: PAH 16 Total µg/L - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:940: PAHs (Sum of total) µg/L 0.21 0.76 - - - - 0.39 0.2 - - - - 6.8 - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:945: PAH 16 Total µg/L - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:945: PAHs (Sum of total) µg/L 5.6 1.5 - - 0.42 - - 2.9 9.6 5.3 0.22 0.4 2.4 19 62 92 1.1 7.6 14 3.5

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:950: PAH 16 Total µg/L - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:950: PAHs (Sum of total) µg/L 0.13 0.25 3 0.05 0.08 0.94 <0.2 0.26 - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:956: Volatile Organic Compounds, asbestos and Polychlorinated Biphenyls data was analysed from 2017 onwards. It is noted that while the 2004 Enviros investigation included speciated PAH analysis, only the sum PAH analytical testing data from this

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:956: investigation is presented here (51No. samples analysed for speciated PAH). This is due to the nature of the data provided for review; as such, while the measured concentrations have been included in the consideration of the human health risk assessment

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:956: for the individual PAH fractions, they have not been included in this screening table.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:958:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:959:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:961:6 The compounds detected are PAH, with a review of the distribution of the remaining PAH for which criteria were available for comparison indicating that they were typically identified in the same location and at similar concentrations. As such, the remaining PAH for which WQS are available for comparison have been

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:961:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:961: Yes(ii) Compounds associated with Polycylic Aromatic Hydrocarbons have been assessed further via and an indicator compound approach. Indicator compounds have been selected based on readily available MRV, WQS for either EQS, DWS or both and following a review of PAH concentrations to ensure they represent the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:961: PAH present. Concentrations of all 16 PAH compounds were measured above the MDL in the leachate and Made Ground. The indicator compounds selected represented a relatively high proportion of the contaminant mass identified. Within the superficial and bedrock, measured PAH concentrations were generally

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:961: lower with some PAH below the MDL. However, at least some of the PAH indicators selected were measured above WQS and/or MDL. As such, The use of indicator compounds for assessment of PAH is considered appropriate to represent the risk from the 16 PAH.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:964:#10:Water Supply (Water Quality) Regulations 2016. Value of 0.1µg/l for PAH split between four individual PAH. Requires summation of

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:966: PAHs (Sum of total) µg/L 2 1 15 - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:966:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-03-LWoW_DQRA.pdf:972: contamination was identified (samples containing sum PAH greater than 1mg/kg were excluded). The SOM was converted

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:7:EPA16 A list of 16 priority PAHs as identified by the USA’s Environmental Protection Agency

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:8:SSI2 holds a COMAH Upper Tier Establishment classification associated with the large quantities of PAH

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:30: 29/06/2016. quantities of PAH on site,

R-2021-1048-FFM-SSI2 Desk Study_Final(1).pdf:42: Coke Oven Gas Main Organics Various PAH’s √ √

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: for the Site, with the risks from asbestos and PAH mitigated by the requirement to import a

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:5: included metals, hydrocarbons including PAH and TPH, inorganics including cyanide,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:7: pathways in relation to asbestos (identified in shallow soils) and PAH (identified in

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:29:buildings or another suitable cover system. The depth at which the PAH exceedances were identified in

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:30:concentration of 1.2mg/kg. The SVOC 2-methylnaphthalene is a type of PAH, with detections of this compound

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:30:corresponding with samples in which the remaining PAH analysed were also measured. The remaining PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:31:A sample from S2-TPA83 at 3m bgl exceeded the GAC for two PAH compounds, which were considered to be

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:31:development. The depth at which PAH were measured in S1-BH13A is such that these pathways are not

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:37:of PAH (including eight compounds within the PAH suite and additionally carbazole, dibenzofuran, 2-

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:37:inorganics, TPH and PAH is required. It is noted that while certain metals are not considered to require further

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:38:detailed assessment. In addition, potentially active pollutant linkages have been identified in relation to PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:39:areas, which will act as a suitable cover system to break the linkages driving risk in relation to PAH and asbestos

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:39:selected metals and inorganics TPH and PAH is required.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:40:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:40:Contaminants associated with the above include metals, hydrocarbons (including tars), PAH, inorganics

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:41:well as potentially present as a result of anthropogenic sources. This includes metals, PAH (which could be

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:41:Associated contaminants with the potential to affect groundwater quality include metals, hydrocarbons, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:Similarly to metals, PAH and TPH are found throughout the Site. Generally, no discernible correlation with

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:albeit on the whole, the measured concentrations of TPH and PAH are likely to be associated with the imported

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:The highest concentrations of sum PAH in the hundreds of mg/kg were measured in S1-BH13A, located in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:S2-TPA83, and as such, the PAH are likely to be associated with the presence of tar.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:42:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:45:The highest concentrations of sum PAH were associated with groundwater samples collected from monitoring

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:45:wells screening Made Ground (maximum concentration of sum PAH of 92µg/l), with maximum measured

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:concentrations of sum PAH concentrations in monitoring wells screening the superficial deposits and bedrock

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:Review of the lateral distribution indicates that concentrations of sum PAH were typically identified in the ones

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:surface material. Concentrations of sum PAH in the northern portion of the Site were typically less than 1µg/l.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:While it appears evident that elevated PAH in the south of the Site are likely associated with the historical land

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:manganese, TPH and PAH. Iron and manganese were identified in soils across the Site, albeit were

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:stocking area). TPH and PAH have also been measured in soils across the Site, again, likely due the Made

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46:Ground. However, isolated elevated concentrations of TPH and PAH have also been identified, which may

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:46: PAH, which were identified across the Site, albeit the highest concentrations were typically identified in the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:51:“For contaminants which are characterised by a high partition coefficient (e.g. some PAH compounds), the rates

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:82: PAH 16 Total mg/kg <16 <16 <22 <41 <16 <120 <50 <16 <16 <100 <16 <16 <17 <56 <16 <16 <16

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:82: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:85: PAH 16 Total mg/kg <22 <16 <309 <26 <18 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16 <16 <16

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:85: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:88: PAH 16 Total mg/kg <16 <16 <18 <47 <16 <16 <16 <26 <16 <16 <16 <16 <16 <153 <16 <16 <16 <68

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:88: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:91: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:91: PAHs (Sum of total) mg/kg 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3 <0.1 <0.1 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:94: PAH 16 Total mg/kg - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:94: PAHs (Sum of total) mg/kg 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:97: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:97: PAHs (Sum of total) mg/kg 0.3 1.8 <0.1 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1 <0.1 - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:100: PAH 16 Total mg/kg - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:100: PAHs (Sum of total) mg/kg <0.1 <0.1 0.26 <0.1 6.3 0.17 <0.1 <0.1 4 <0.1 3 - <0.1 <0.1 - <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:103: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:103: PAHs (Sum of total) mg/kg <0.1 <0.1 3.1 <0.1 <0.1 <0.1 - 7 - 0.22 0.16 <0.1 - 2.1 0.56 9.3 - 0.33 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:106: PAH 16 Total mg/kg -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:106: PAHs (Sum of total) mg/kg -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:109: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:109: PAHs (Sum of total) mg/kg - - - - - - - - - <0.1 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:112: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:112: PAHs (Sum of total) mg/kg 2.5 <14.91 2.9 0.44 0.44 <0.1 2.5 <0.1 <0.1 - 5.8 2.6 <0.1 - 7 0.4 - 31 <0.1

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:115: PAH 16 Total mg/kg - - - - 0.15 4.4 4.3 0.37 25 2.3 0.31 4.2 2.2 1.1 3.4 9.8 0.12 1.6 0.71

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:115: PAHs (Sum of total) mg/kg 0.53 - 8.1 0.8 - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:118: PAH 16 Total mg/kg 0.05 3.6 0.35 1.1 0.67 - 1.8 - 0.63 - - 0.18 16 0.05 4.5 - 1.1 - 1.4

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:118: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:121: PAH 16 Total mg/kg 29

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:121: PAHs (Sum of total) mg/kg -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:124: PAH 16 Total mg/kg 3.9 0.57 0.8 33 0.8 0.8 21 0.8 0.8 0.8 - 38 1.8 330 29 0.8 13 8.6 21

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:124: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:127: PAH 16 Total mg/kg 1.5 0.26 1.1 7.3 0.74 14 0.05 - - 34 1.1 - 30 6 0.05 8.2 3.2 1.6 0.57

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:127: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:130: PAH 16 Total mg/kg 0.61 - 38 1.8 5 0.05 9.6 4.1 - 0.34 0.05 2.4 0.53 3.2 - 0.05 - 0.05 0.67

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:130: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:133: PAH 16 Total mg/kg - - 7.7 1.5 - - - - 1.6 - - - - - - - 0.99 10 7.7

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:133: PAHs (Sum of total) mg/kg 1.3 <0.1 - - - 5.8 - 1.6 - - 1.9 0.91 97 - 3.9 - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:136: PAH 16 Total mg/kg 1.2 0.75 0.05 - 0.49 0.16 15.94 0.05 1.8 0.05 2.7 2.5 2.1 0.05 1.1 0.05 - 0.55 0.56

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:136: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:139: PAH 16 Total mg/kg 0.05 0.05 1.1 4.1 - 0.2 11 0.05 1.1 0.05 10 1.4 6.4 0.05 38 150 44 0.21 0.15

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:139: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:142: PAH 16 Total mg/kg 38 670 43 27 - 0.05 1.8 0.05 6.8 0.21 0.05 1.7 1.2 0.05

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:142: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:146: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:147: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:148: PAHs (Sum of total) µg/L - - 15 - - - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:150: PAH 16 Total µg/L <160 <160 <160 - - - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:150: PAHs (Sum of total) µg/L - - - <0.2 0.26 0.61 <0.2 0.63 0.28 0.39 <0.2 0.38 0.36 0.52 0.23 0.22 0.5 0.21

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:155: PAH 16 Total µg/L - - - - - - - - - - - - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:155: PAHs (Sum of total) µg/L 9.6 5.3 0.22 0.4 2.4 19 62 92 1.1 7.6 14 3.5 0.13

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:160: Volatile Organic Compounds, asbestos and Polychlorinated Biphenyls data was analysed from 2017 onwards. It is noted that while the 2004 Enviros investigation included speciated PAH analysis, only the sum PAH analytical testing data from this

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:160: investigation is presented here (51No. samples analysed for speciated PAH). This is due to the nature of the data provided for review; as such, while the measured concentrations have been included in the consideration of the human health risk assessment

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:160: for the individual PAH fractions, they have not been included in this screening table.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:162:6 The compounds detected are PAH, with a review of the distribution of the remaining PAH for which criteria were available for comparison indicating that they were typically identified in the same location and at similar concentrations. As

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:162: such, the remaining PAH for which WQS are available for comparison have been selected as indicator compounds.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:162:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:162: Yes (i) Compound considered to be associated with Polycylic Aromatic Hydrocarbon, with the exception of free cyanide. As such, these compounds have been assessed further indirectly through indicator compounds (either PAH or total

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:165:#10:Water Supply (Water Quality) Regulations 2016. Value of 0.1µg/l for PAH split between four individual PAH. Requires summation

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:167: PAHs (Sum of total) µg/L 1 1 15 - -

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:167:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0428-01-Net_Zero_DQRA.pdf:172: contamination was identified (samples containing sum PAH greater than 1mg/kg were excluded). The SOM was converted

R-2021-1048-FFM-CON LAND 1048.pdf:2:SPR linkage including Asbestos, PAH and NAPL with further consideration of the

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: bitumen and PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: casting, tars, PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:13: macadam works and slag wool works immediately east, with Those above plus TPH, PAH and

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: GRO,BTEX, Phenols, PAH

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: CH2M-SSI1 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: CH2M – SSI2 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Within SSI Landholdings Sulphate, Chloride TPH, BTEX, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22:criteria adopted, with localised exceedances for PAH, lead and zinc.

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Former industrial uses - iron and steel making plant Phenols, PAH, VOC, SVOC, PCB

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Asbestos, TPH, BTEX, Phenols, PAH, VOC, SVOC

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Railways Asbestos, hydrocarbons, ash, PAH, phenol, sulphates

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Phenols, PAH, VOC, SVOC, PCB, ammoniacal nitrogen

R-2021-1048-FFM-Factual Report SSI 1.pdf:375: (730 days), PAH MS (14 days), PCB (30 days), pH +

R-2021-1048-FFM-Factual Report SSI 1.pdf:375: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual Report SSI 1.pdf:399: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual Report SSI 1.pdf:411: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual Report SSI 1.pdf:411: days), Organic Matter (Manual) (730 days), PAH MS

R-2021-1048-FFM-Factual Report SSI 1.pdf:411: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual Report SSI 1.pdf:412: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-Factual Report SSI 1.pdf:432: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-Factual Report SSI 1.pdf:433: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-Factual Report SSI 1.pdf:433: 2:1 (365 days), Naphthalene, PAH FID

R-2021-1048-FFM-Factual Report SSI 1.pdf:433: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-Factual Report SSI 1.pdf:434: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-Factual Report SSI 1.pdf:467: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-Factual Report SSI 1.pdf:476: Naphthalene (14 days), PAH MS (14 days), pH +

R-2021-1048-FFM-Factual Report SSI 1.pdf:489: days), Organic Matter (Manual) (730 days), PAH MS

R-2021-1048-FFM-Factual Report SSI 1.pdf:489: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:17:Levels of PAH were measured above the screening criteria in three locations, the SPL linkage for these

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:24: from materials impacted with asbestos, and PAHs; and,

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:32:Where contaminants other than asbestos or NAPL (such as PAH and the pollutant linkages identified

R-2021-1048-FFM-10035117-AUK-XX-XX-RP-ZZ-0417-05-Rem_Strat_LWoW.pdf:43:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:6:screening criteria. Exceedances of Boron, Chromium, PAHs and Vinyl Chloride have also been noted,

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:6:Boron and PAH’s are leaching from the Made Ground in concentrations sufficient to impact

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:14: PAH 17 Total Non-Normal 146 <0.10 - 5.61

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:21: PAH 16 Total Non-Normal 65 < 0.10 - 281.82

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:25:2017. The samples were tested for heavy metals, inorganics, TPH and PAH, VOCs, SVOCs and

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:26: PAHs

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:27: PAH Total 12 ug/l <0.04 21 ‐ ‐

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:28:Exceedances of boron, benzene, chromium, PAHs, TPHs and vinyl chloride are also noted, and are

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:28:were below current screening criteria. Exceedances and Boron and some PAHs were also recorded.

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:28:The results of the water sampling would suggest that zinc, and to a lesser extent boron and PAHs are

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:54:screening criteria. Exceedances of Boron, Chromium, PAHs and Vinyl Chloride have also been noted,

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:54:Boron and PAH’s are leaching from the Made Ground in concentrations sufficient to impact

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:473: (730 days), PAH MS (14 days), PCB (30 days), pH +

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:473: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:497: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:509: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:509: days), Organic Matter (Manual) (730 days), PAH MS

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:509: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:510: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:530: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:531: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:531: 2:1 (365 days), Naphthalene, PAH FID

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:531: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:532: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:565: Matter (Manual) (730 days), PAH

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:574: Naphthalene (14 days), PAH MS (14 days), pH +

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:587: days), Organic Matter (Manual) (730 days), PAH MS

R-2021-1048-FFM-GEO_STDCO_GEOENVIRONMENTALSUMMARYREPORT(002)sm.pdf:587: (730 days), PAH MS (14 days), pH + Conductivity (7

R-2021-0100-CD-COMPLIANCE OFFFICER REPORT.pdf:3:elevated concentrations of PAHs but due to the ongoing remediation works are

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000006_App_C.pdf:1: See PAH

R-2021-0100-CD-MGE04321 Cont Land.pdf:3:elevated concentrations of PAHs but due to the ongoing remediation works are

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:66: PAH is extracted from one litre of filtered water sample by

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:66: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:66: Note for PAH by SPE

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: dichloromethane (DCM) using sonication. The PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: concentration is recorded both as “Total PAH” and as

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: PAH concentration is recorded both as “Total PAH” and

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:85: 3302 1.6 mg/kg Total PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: The PAHs in the soil sample are extracted into hexane:

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000005_App_B-2_Part2.pdf:86: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:12:for human health. Concentrations of arsenic, total cyanide and PAHs were measured above their respective

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:12:Multiple CoC including metals, total cyanide, ammoniacal nitrogen, TPH, PAH, phenol, xylene and 1,2-

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:20:Holme Beck were generally less than the applicable EQS with the exception of two PAH compounds which

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:heavy metals, inorganic compounds and PAHs have been identified in the subsurface at concentrations which

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:24:such as PAHs, including naphthalene. A number of options for the remediation of this gross contamination

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment.pdf:26:measured in Holme Beck were generally less than the applicable EQS with the exception of two PAH

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:12:Concentrations of PAH were measured in 4 of the 5 samples analysed and concentrations of TPH were

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:Low levels of PAH were measured in the majority of samples with higher concentrations recorded in

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:22:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:22:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: PAH is extracted from one litre of filtered water sample by

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: Note for PAH by SPE

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: dichloromethane (DCM) using sonication. The PAH

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: concentration is recorded both as “Total PAH” and as

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: PAH concentration is recorded both as “Total PAH” and

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: 3302 1.6 mg/kg Total PAH

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: The PAHs in the soil sample are extracted into hexane:

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0100-CD-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:49: PAH is extracted from one litre of filtered water sample by

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:49: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:49: Note for PAH by SPE

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: dichloromethane (DCM) using sonication. The PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: concentration is recorded both as “Total PAH” and as

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: PAH concentration is recorded both as “Total PAH” and

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:68: 3302 1.6 mg/kg Total PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: The PAHs in the soil sample are extracted into hexane:

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000004_App_B-1_Part12.pdf:69: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0100-CD-Phase II ESA.pdf:24: including tars, PAH, cyanides, thiocyanate, volatile

R-2021-0100-CD-Phase II ESA.pdf:24: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2021-0100-CD-Phase II ESA.pdf:24: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2021-0100-CD-Phase II ESA.pdf:24: Railways and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, and pH.

R-2021-0100-CD-Phase II ESA.pdf:24: Above Ground Storage tanks (various) TPH, PAH, pH.

R-2021-0100-CD-Phase II ESA.pdf:24: Metals, asbestos, TPH, PAH, VOC, SVOC,

R-2021-0100-CD-Phase II ESA.pdf:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0100-CD-Phase II ESA.pdf:25: Metals, TPH, PAHs, VOC, SVOC, cyanide, thiocyanate,

R-2021-0100-CD-Phase II ESA.pdf:25: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2021-0100-CD-Phase II ESA.pdf:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0100-CD-Phase II ESA.pdf:25: Water resources – Metals, ammoniacal nitrogen and PAH

R-2021-0100-CD-Phase II ESA.pdf:26:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2021-0100-CD-Phase II ESA.pdf:29:Concentrations of PAH were measured in 90 of the 101 samples analysed. Statistical analysis indicates that,

R-2021-0100-CD-Phase II ESA.pdf:29:within granular made ground, PAH concentrations were an order of magnitude higher than within slag dominant

R-2021-0100-CD-Phase II ESA.pdf:29:Made Ground. Concentrations of PAH measured in cohesive Made Ground were a further order of magnitude

R-2021-0100-CD-Phase II ESA.pdf:30:Leached concentrations of PAH were measured in all samples analysed and comprised a broad range of both

R-2021-0100-CD-Phase II ESA.pdf:32:Where PAHs or TPH were detected they were generally measured only marginally above the MDL with the

R-2021-0100-CD-Phase II ESA.pdf:40:The concentrations measured by third parties in excess of the GAC were all PAHs and are in line with the

R-2021-0100-CD-Phase II ESA.pdf:42:of PCBs, PAHs and carbazole in soil via the vapour inhalation pathway – driven by vapour intrusion (pollutant

R-2021-0100-CD-Phase II ESA.pdf:48:Concentrations of heavy metals, ammoniacal nitrogen, TPH, PAH and phenol were measured in excess of

R-2021-0100-CD-Phase II ESA.pdf:52:Concentrations of manganese and PAHs have been measured in excess of WQS in more than half of the

R-2021-0100-CD-Phase II ESA.pdf:52:of their MDL: magnesium, sulphate, sulphur, chloride, free cyanide, thiocyanate, selected PAHs, styrene,

R-2021-0100-CD-Phase II ESA.pdf:53:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2021-0100-CD-Phase II ESA.pdf:53:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2021-0100-CD-Phase II ESA.pdf:53:screening the Made Ground and the superficial deposits. The highest concentrations of TPH, PAH and VOCs

R-2021-0100-CD-Phase II ESA.pdf:56:including slag materials) and groundwater were assessed using GAC. Concentrations of arsenic and PAHs

R-2021-0100-CD-Phase II ESA.pdf:56:Concentrations of arsenic, total cyanide and PAHs will need to be considered in the remedial strategy for the

R-2021-0100-CD-Phase II ESA.pdf:72:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0100-CD-Phase II ESA.pdf:73: PAH (ex. Naphthalene)

R-2021-0100-CD-Phase II ESA.pdf:74:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0100-CD-Phase II ESA.pdf:494: Total PAH 14 2600 0.05 254 652

R-2021-0100-CD-Phase II ESA.pdf:495: Total PAH 70 110000 0.05 1722 12974

R-2021-0100-CD-Phase II ESA.pdf:496: Total PAH 5 14 0.49 4.26 4.97

R-2021-0100-CD-Phase II ESA.pdf:497: USEPA 16 PAH 6 1700 0.05 214 562

R-2021-0100-CD-Phase II ESA.pdf:509: PAHs

R-2021-0100-CD-Phase II ESA.pdf:509: PAH - USEPA 16, Total DETSC 3303 0.1 mg/kg 5.9 8.3 14

R-2021-0100-CD-Phase II ESA.pdf:512: PAHs

R-2021-0100-CD-Phase II ESA.pdf:512: PAH - USEPA 16, Total DETSC 3303 0.1 mg/kg < 0.10 72 760

R-2021-0100-CD-Phase II ESA.pdf:657: PAHs

R-2021-0100-CD-Phase II ESA.pdf:657: PAH Total DETSC 3304 0.2 ug/l 3.1 110 0.65

R-2021-0100-CD-Phase II ESA.pdf:660: PAHs

R-2021-0100-CD-Phase II ESA.pdf:660: PAH Total DETSC 3304 0.2 ug/l 0.62 7800 11

R-2021-0100-CD-Phase II ESA.pdf:663: PAHs

R-2021-0100-CD-Phase II ESA.pdf:663: PAH Total DETSC 3304 0.2 ug/l 4.3 4.1 1.1

R-2021-0100-CD-Phase II ESA.pdf:680: PAHs

R-2021-0100-CD-Phase II ESA.pdf:680: PAH Total DETSC 3304 0.2 ug/l 2900 110 70

R-2021-0100-CD-Phase II ESA.pdf:683: PAHs

R-2021-0100-CD-Phase II ESA.pdf:683: PAH Total DETSC 3304 0.2 ug/l 13000 22 840

R-2021-0100-CD-Phase II ESA.pdf:720: WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2021-0100-CD-Phase II ESA.pdf:720: PAH MS (4 days), EPH (4 days)

R-2021-0100-CD-Phase II ESA.pdf:720: 050 0.50 WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2021-0100-CD-Phase II ESA.pdf:720: PAH MS (4 days), EPH (4 days)

R-2021-0100-CD-Phase II ESA.pdf:721: 100 1.00 WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2021-0100-CD-Phase II ESA.pdf:721: PAH MS (4 days), EPH (4 days)

R-2021-0100-CD-Phase II ESA.pdf:725: days), Nitrite as N (2 days), PAH MS

R-2021-0100-CD-Phase II ESA.pdf:726: days), Nitrite as N (2 days), PAH MS

R-2021-0100-CD-Phase II ESA.pdf:726: days), Naphthalene (14 days), PAH

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:23:Based on the ratio of genotoxic PAHs to benzo(a)pyrene, the surrogate marker approach for genotoxic PAHs

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:24: used for the relevant PAHs;

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:24:TPH concentrations were predominantly recorded below laboratory detection limits. PAH concentrations were

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:26: PAHs

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:28: PAHs

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:31:Exceedances of PAHs are recorded up to a maximum of five orders of magnitude above the EQS. Whilst

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:31:development and the elevated concentrations of PAHs recorded, there is likely to be a potentially unacceptable

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:52:Exceedances of PAHs are recorded up to a maximum of five orders of magnitude above the freshwater EQS.

R-2021-0100-CD-STDC_HWY-ATK-HGT-PR-RP-CE-000001_C01.pdf:52:proposed development and the elevated concentrations of PAHs recorded, there is likely to be a potentially

R-2021-0753-FFM-Arcadis - South Bank Strategy.pdf:10: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:9: PAHS.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:26:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:26: PAHs, phenol and TPH. Were taken from within the site boundary

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:26: sulphate cyanide and PAHs, phenol and TPH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:27: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:27: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:41:  Railway ballast containing metals and PAHs,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:41: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:42: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:42: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:43: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:43: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:44: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:44: exception of PAH results.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:44: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:44: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:45: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:56: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:56: westerly direction (towards the Tees). The pH was alkaline. TPH and PAHs were below detection, but copper

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:57: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:57: westerly direction (towards the Tees) The pH was alkaline. TPH and PAHs were below detection limits, but

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:77: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:77:  PAHs – 1 sample (GAC 40mg/kg)

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:87: hydrocarbons, PAHs and BT

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:92:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s, VOCs, SVOCs and aromatic

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:92:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282515 BH03TP 2.00 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282516 BH03TP 5.00 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282517 BH04TP 2.00 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282518 BH04TP 3.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282519 BH05TP 4.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282520 TP01 0.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282521 TP01 2.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282522 TP02 1.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282523 TP02 2.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282524 TP05 2.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:257:1282525 TP05 0.00-1.50 SOIL 20/12/17 GJ 250ml x2, GJ 60ml x2, PT 1L x2 Naphthalene (14 days), PAH MS (14 days), pH +

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:270: PAHs

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:270: PAH - USEPA 16, Total 0.1 mg/kg 0.49 2.9 0.5 1.1 < 0.10 1.4 0.21 1.5 3.9 7.2 10 15 0.44 1.2 1.9 0.92 21 2.7 570 11 0.75 1.1 13000 1.5 0.23 0.18 0.61 0.43 150 < 0.10 < 0.10 2.4 14 0.18 0.31 2200 0.31 0.6 1.3 1 0.72 < 0.10

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:330:of PAH contained within the Coke Oven Gas Main which also applies to TS4. Other COMAH products

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:376:of PAH contained within the Coke Oven Gas Main. This classification also applies to the TS4 site.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:378:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:379:  Hydrocarbons – PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:379:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:380:  Hydrocarbons ‐ TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:381:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:381:  Hydrocarbons ‐ PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:381:  Hydrocarbons ‐ TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:382:  Hydrocarbons ‐ PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:383:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:384:  Hydrocarbons – PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:385:  Hydrocarbons ‐ PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:385:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:386:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:386:  Hydrocarbons ‐ TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:387:  Hydrocarbons – PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:388:  Hydrocarbons ‐ PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:388:  Hydrocarbons – TPH and PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:390: PAH                 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:392: PAH (total) N/A 15 <10 16 0 ‐ ‐

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:394: PAH (total) * mg/l <0.01 46.18 12.38

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:394:has been linked to TS4. Elevated levels of PAH are also associated with BHC5. All four water samples

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:394:of the By‐Products Plant and SBCO, which are the most likely sources of Phenol and PAH (total).

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:396: PAH Total EPA16 15 <16 <100 36.8 <16 145483 25534.86 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:398: PAH Total EPA16 15 <16 120 20.8 <16 34 22.7 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:The results show exceedances of PAH Total EPA16 within Area 1 which is likely to be associated with the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:known as BTEX, as well as PAH total EPA16 and TPH (C8‐C37). Area 2 includes the By‐Products Plant of

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:Exceedances of TPH (C8‐C37) and PAH total EPA16 were also recorded within Area 3 within which the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:with PAH also associated as a by‐product of fuel from burning. On closer review the results exceeding

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:400:source. Exceedances of PAH EPA total 16 are recorded throughout Area D at depths of between 0.2m

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:402: PAH Total *

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:403:Products Plant reported elevated TPH GC, Gasoline Range Organic, PAH Total EPA 16 and BTEX are most

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:404: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:404: Hydrocarbons – oil and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:405: maintenance PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:405: ‐ fuels, oil and grease PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:405: PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:405: Hydrocarbons – oils and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:406: Hydrocarbons – oils and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:406: Hydrocarbons – fuel, oils and PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:406: Hydrocarbons – oil and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:406: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:406: ‐ degreasing Hydrocarbons – oils and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:407: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:407: Hydrocarbons – oils and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:407: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:407: maintenance PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:408: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:408: Hydrocarbons –oils and grease PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:409: PAH 

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:411: Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:411: Hydrocarbons ‐ PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:412: Fuel, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:412: Car parks and highways Fuels, oil and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:412: Fuels, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:412: Fuels oils and grease Hydrocarbons – TPH & PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:413: Fuel, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:413: Fuels, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:413: Oils and grease Hydrocarbons ‐ PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:413: Diesel fuel Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:414: Oils and grease Hydrocarbons ‐ PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:414: Fuels, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:415: Oils and grease Hydrocarbons ‐ PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:415: Fuels, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:415: Oils and grease Hydrocarbons – PAH and TPH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:416: Oils and grease Hydrocarbons – PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:416: Fuel, oils and grease Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:416: Oils and grease Hydrocarbons ‐ PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:416: Oils and grease Hydrocarbons – PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:417: “Jallop” – COMAH Hydrocarbons – TPH and PAH   Mod

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:494:plastic bottle, 2 x 1litre amber glass bottles (for TPH and PAH) and 1 x 40ml glass vial (for

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:545: Polycyclic Aromatic Hydrocarbons (PAH) EPA16 PAHFID 1mg/k

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:545: Polycyclic Aromatic Hydrocarbons (PAH) EPA16 PAHFID 0.01 m

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:548: Total PAH EPA-16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:549:Spike studies were carried out on the granular waste matrix for PAH and TPH analysis, see separate notes.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:550:Total PAH EPA-16 mg/kg 349 V <2 <2

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:552:Spike studies were carried out on the granular waste matrix for PAH and TPH analysis, see separate notes.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:553:Total PAH EPA-16 mg/kg 349 V 8.1 25.0 21.0 2.6 8.2 6.7

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:555:validation batch of spikes for PAH and TPH analysis was carried out.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:555:NOTE: The TPH and PAH results have not been blank corrected.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:555:Acceptable spike recoveries have been achieved for both PAH and TPH methods on the granular waste matrix.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:557:Total PAH ug/l <2 <2 <2

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:558:Total PAH ug/l <2 <2

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:560:Total PAH ug/l <2

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:585: Total PAH EPA-16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:586: Total PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:603:amber glass bottles (for TPH and PAH) and 1 x 40ml glass vial (for VOCs). Samples will be labelled and a

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:633: PAHFID

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:633: Polycyclic Aromatic Hydrocarbons (PAH) EPA16 PAHFID 1mg/kg (soil), 0.01

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:645: bottles (for TPH, and PAH) and 40ml glass vials (for VOCs).

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:645: glass bottles (for TPH, and PAH) and 40ml glass vials (for VOCs).

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:651: 16 ü sulphates and PAH’s

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:657: Elevated levels of Total PAH were detected in only one sample (184 mg/kg –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:657: 11AT4A, 0.3 m bgl). The 95 percentile calculated for Total PAH (18 mg/kg)

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:658:DIV 40 mg/kg PAH Total EPA16 17.91 <16 <16 <16 <16 <184 <16 <18 <18 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:659:DIV 40 mg/kg PAH Total EPA16 17.91 <16 <16 <16 <16 <16 <28

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:661: Elevated levels of Total PAH were detected in six samples (12AT8, 2.0m bgl;

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:661: and, 12AT17, 0.3m bgl). PAH values exceeding guideline values range from

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:661: percentile calculated for Total PAH (31 mg/kg) is below the guideline value of

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:662:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <120 <16 <16 <100 <41 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:663:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <56 <16 <16 <16 <16 <17 <16 <22 <50

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:664:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <16 <16 <16 <16 <17 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:665:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <309 <22 <18 <26 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:667: Elevated levels of Total PAH were detected in two locations (47 mg/kg –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:667: calculated for Total PAH (19.5 mg/kg) was well below the guideline value of 40

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:668:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:669:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16 <16 <16 <16 <18 <47 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:670:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <38 <16 <26 <16 <16 <16 <16 <16 <153

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:671:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:673: Slightly elevated levels of Total PAH were detected at three locations (4 2

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:673: 4.0 m bgl). The 95 percentile calculated for Total PAH (26.07 mg/kg) was

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:674:DIV 40 mg/kg PAH Total EPA16 26.07 <42 <16 <16 <16 <44 <16 <27 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:675:DIV 40 mg/kg PAH Total EPA16 26.07 <16 <16 <16 <68 <18 <16 <32 <34

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:678: Elevated levels of Total PAH were detected in five samples (48 mg/kg –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:678: The 95th percentile calculated for Total PAH (19.5 mg/kg) across the whole of

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:679:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <32 <16 <28 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:680:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <17 <38.45 <16 <16 <17 <16 <31 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:681:DIV 40 mg/kg PAH Total EPA16 19.45 <48 <16 <96 <20 <16.07 <16 <20.88 <16 <16 <19.97

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:682:DIV 40 mg/kg PAH Total EPA16 19.45 <19.87 <40.82 <18.6 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:683:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:684:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <16 <16 <16 <52 <16 <23 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:685:DIV 40 mg/kg PAH Total EPA16 19.45 <20 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:688:DIV 40 mg/kg PAH Total EPA16 <16 <31 <16 <27 <27 <16 <16 <29 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:690: Elevated levels of Total PAH were detected in seven samples across the area,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:690: (17AT5, 4.0 m bgl). The 95 percentile calculated for Total PAH across Area

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:691:DIV 40 mg/kg PAH Total EPA16 28.28 <19 <16 <16 <17 <25 <74 <16 <16 77.0 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:692:DIV 40 mg/kg PAH Total EPA16 28.28 <43 <16 <16 <16 <18 <21 <23 <16 <16 <422

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:693:DIV 40 mg/kg PAH Total EPA16 28.28 <25 <16 <16 <32 <16 <35 <25 <104 <16 <28

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:694:DIV 40 mg/kg PAH Total EPA16 28.28 <21 <16 <39 <16 <19 <16 <16 <17 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:695:DIV 40 mg/kg PAH Total EPA16 28.28 <16 <16 342.0 298.0 <18

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:697:DIV 0.82 mg/l PAH Total EPA16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:697:NB. DIV for PAH is for sum of ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:701:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:701:NB. DIV for PAH is for sum of ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:702:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:702:NB. DIV for PAH is for sum of ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:704: • PAH’s were elevated in the ground at shallow and deep samples primarily in

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:706: phenols, sulphates and PAH’s

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:710: In Area 7, elevated levels of Total PAH were detected in only one sample

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:710: (7AT1, 1.5m bgl – 51 mg/kg). The 95 percentile calculated for Total PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:711:DIV 40 mg/kg PAH Total EPA16 18.10 <16 <16 <51 <31 <16 <16 <17 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:712:DIV 40 mg/kg PAH Total EPA16 18.10 <18 <17 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:714: Elevated levels of Total PAH were detected in only one sample (377 mg/kg –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:714: 8AT3, 0.2 m bgl). The 95 percentile calculated for Total PAH (18 mg/kg) was

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:715:DIV 40 mg/kg PAH Total EPA16 17.58 <16 <16 <16 <24 <377 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:717: Elevated levels of Total PAH were detected in two locations (169 mg/kg –

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:717: for Total PAH (29 mg/kg) was below the guideline value of 40 mg/kg.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:718:DIV 40 mg/kg PAH Total EPA16 28.75 <16 <16 <169 <61

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:722:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <5

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:722:NB. DIV for PAH is for sum of ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:724: apart from isolated levels of PAHs in the shallow soils, which are most likely as

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:726: H ü contain metals, phenols, sulphates and PAH’s

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:731: Levels of Total PAH in excess of guideline criteria were detected in seven

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:731: bgl). The 95th percentile calculated for Total PAH (43.69 mg/kg) exceeds the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:732:DIV 40 mg/kg PAH Total EPA16 43.69 <40 <20 <100 <16 <20 <19 <19 <16 <21 <50

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:733:DIV 40 mg/kg PAH Total EPA16 43.69 <21 <61 <37 <20 85.0 <21 <16 <16 <61 139.0

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:734:DIV 40 mg/kg PAH Total EPA16 43.69 <77 <16 <18 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:736: Levels of Total PAH in excess of guideline values were detected in fifteen

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:736: m bgl). The 95th percentile calculated for Total PAH (2,167 mg/kg) across all

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:737:DIV 40 mg/kg PAH Total EPA16 2167.24 <7043 <166 20780.0 <47 <16 <72 <17 <18 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:738:DIV 40 mg/kg PAH Total EPA16 2167.24 <34 <16 <327 <18 <81 <62 <75 <39 418.0 <23

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:739:DIV 40 mg/kg PAH Total EPA16 2167.24 4196.0 <16 658.0 145483.0 <87 <16 <50 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:741: Elevated levels of Total PAH in excess of guideline criteria were detected in

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:741: 4 6 m g / k g (3AT6 (3.5 m bgl). The 95th percentile calculated for Total PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:742:DIV 40 mg/kg PAH Total EPA16 43.41 <16 <400 <18 <17 <16 <16 <89 <18 <46 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:744: Levels of Total PAH in excess of guideline criteria were detected in five

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:744: percentil e calculated for Total PAH (236.76 mg/kg) across A r e a 4 exceeded

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:745:DIV 40 mg/kg PAH Total EPA16 236.76 <16 <389 <17 <465 <47 179.0 <16 <17 <470 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:747: Elevated levels of PAH were observed in five samples across Area D ranging

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:748:DIV 40 mg/kg PAH Total EPA16 19.07 <34 <18 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:749:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 <38 <16 <16 <16 <20

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:750:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 120.0 <19 <16 <16 <17

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:751:DIV 40 mg/kg PAH Total EPA16 19.07 <18 <16 <16 <18 <16 <23 <16 <18 <16 <58

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:752:DIV 40 mg/kg PAH Total EPA16 19.07 <20 103.0 <16 <19 <16 <19 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:753:DIV 40 mg/kg PAH Total EPA16 19.07 <18 <49 <16 <16 <16 <16 <16 <16 <18 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:754:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:755:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <45 <36 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:758: Levels of Total PAH in excess of guideline values were detected in ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:758: levels of Total PAH ranging from 41 mg/kg (ECT41, 0.6m bgl) to 209 mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:758: In sub-A rea D there were six samples with elevated levels of Total PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:759:DIV 40 mg/kg PAH Total EPA16 25.30 <26 <40 <20 <16 <16 <32 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:760:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <16 <16 <16 <17 <16 <16 <18 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:761:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <40 <18 <16 <16 <16 <16 <16 <37 <60

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:762:DIV 40 mg/kg PAH Total EPA16 25.30 <18 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:763:DIV 40 mg/kg PAH Total EPA16 25.30 <77 <209 <16 <41 <26 <26 <18 <16 <18 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:764:DIV 40 mg/kg PAH Total EPA16 25.30 <22 <29 <18 <16 <30 241.0 237.0 <55 <17 <37

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:765:DIV 40 mg/kg PAH Total EPA16 25.30 <52 <29 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:766:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <16 <48 <17 <16 <76 <18

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:769:DIV 40 mg/kg PAH Total EPA16 36.00 <16 <36 <39 <16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:771: Five groundwater samples contained PAHs in concentrations exceeding the

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:771: 95 percentile calculated for PAHs of 2.95 mg/l exceeds the guideline value of

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:772:DIV 0.8 mg/l PAH Total EPA16 2.95 <83.55 <0.21 <0.18 <7.11 <1.67 <0.17 <4.34 <0.33 <0.16 1.5 <0.16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:772:NB. DIV for PAH is for sum of ten

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:774: • Hydrocarbons including PAHs, BTEX Compounds and TPH were identified in

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:777: • Locally elevated PAH levels in excess of guideline criteria were found

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:777: • The bulk oil tank s near the Blast Furnace; Elevated PAHs and BTEX occurred

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:777: • The SLEMS area; PAHs, and BTEX exceeded the Tier 1 soil screening criteria

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:777: groundwater samples were in excess of screening values for BTEX, PAH, GRO

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:778: PAH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:778: PAH Polyaromatic Hydrocarbons

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:794: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:796: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:798: SO Zn D-A-T11 D B SO SO 3-A-B2 PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:804: PA PAH Total EPA16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:813: criteria. PAH concentrations were also elevated in soils from the eastern area of 12

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:819: from isolated levels of PAHs in the shallow soils, which are most likely as a result

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:823: Elevated concentrations of PAH, BTEX compounds and, to a lesser degree TPH,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:827: contaminants (TPH, PAH and BTEX Compounds 8 ). The occurrence of elevated

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:827:8 TPH – Total Petroleum Hydrocarbons; PAH- Poly Aromatic Hydrocarbons; BTEX Compounds – Benzene,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:835: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:841: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:847: SO Zn D-A-T11 D B SO SO 3-A-B2 PA PAH Total EPA16 DIV 40mg/kg

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:849: PA PAH Total EPA16

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:859:storage and use hydraulic fluid, ingestion, inhalation Medium E levated soil PAH in nort h and eastern portions of the area, Low

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:863:s t o r a g e a nd hydraulic fluid, ingestion, inhalation Medium Slightly elevated levels of PAH detected in soils, and elevated TPH

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:863: Mild migration. Elevated levels of TPH and PAH identified in soil and

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:869: Mild migration. Limited elevated levels of metals and PAH i n

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:869: and gravel Mild underlying sands. Limited elevated levels of metals and PAH in

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:873:use greases and solvents utilised. Elevated PAH detected in one soil samples, although

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:873: permeable strata Mild migration. Limited elevated soil PAH detected, however no

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:875: phytotoxic and heavy utilised. Elevated levels of PAHs detected at two locations.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:875:use greases and solvents utilised. Elevated levels of PAHs detected at two locations .

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:878: creosote, tar, ingestion, inhalation Medium Locally elevated soil PAH in shallow and deep soil , source not

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:878: permeable strata Mild migration. Locally elevated soil PAH in shallow and deep soil,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:880: creosote, tar, ingestion, inhalation Medium Locally elevated s o i l PAHs and BTEX compounds at eastern side of Low

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:880: (River Tees) permeable strata water Locally elevated soil PAHs and BTEX compounds at east ern side of Low

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:881: (Estuarine and permeable strata groundwater Locally elevated soil PAHs and BTEX compounds at eastern side of

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:881: Marine Alluvium Mild site. Similarly elevated hydrocarbons in groundwater; PAHs, BTEX,

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:881: receptors (Tees drainage or sensitive SSSI E levated hydrocarbons in groundwater; PAHs, BTEX, GRO, TPH.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:885:(Area 2) creosote, tar, ingestion, inhalation Medium Locally elevated soil PAHs and BTEX compounds in soil. Site Low

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:885: (River Tees) permeable strata water Locally elevated soil PAHs and BTEX in soil . Open areas allow Low

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:886: (Estuarine and permeable strata groundwater Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:886: receptors (Tees drainage or s e n s i t iv e S S S I Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:886: (i.e. land which drainage or adjacent land values Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:887:storage and hydraulic fluid, ingestion, inhalation Medium Locally elevated soil PAHs and BTEX compounds in soil. Site

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:887: (River Tees) permeable strata water Locally elev a t e d soil PAHs and BTEX in soil . Open areas allow

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:892:work was 15th June, allowing a 13-week programme. zinc, boron; organics - TPH, PAH and BTEX compounds3.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:892:3 TPH: Total Petroleum Hydrocarbons; PAH: Poly-Aromatic Hydrocarbons: BTEX Compounds; Benzene, Toluene, Ethyl-benzene and Xylene.

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:893:Elevated concentrations of PAH, BTEX compounds and, to a workers engaged in excavation

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:895:Lackenby Works apart from isolated levels of PAHs in the Receptors pathway is direct however

R-2020-0357-OOM-South Industrial Zone ES - Vol 3 - Appendix H - July 2020.pdf:898:and boron, were found in excess of screening criteria. PAH

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:20: metals, pH, sulphate cyanide and PAHs, phenol

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:20: cyanide and PAHs, phenol and TPH

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:25: contamination (and potentially natural organics) such as PAHs and TPH but is no longer

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:26:H4.57 TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:26:H4.58 The results of chemical analysis for metals and PAHs benzo(a)pyrene and naphthalene in 11 soil

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:28:H4.66 A range of metals, phenols, aliphatic hydrocarbons, PAH’s, VOCs, Semi Volatile Organic

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:28:H4.67 A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:36: PAHs) determinands and there is therefore a requirement for its collection and treatment prior

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter H - July 2020.pdf:43: 17 PAH Polycyclic Aromatic Hydrocarbons

R-2020-0357-OOM-South Industrial ES - Vol 2 - Chapter G - July 2020.pdf:32: of sulphates, cyanide, arsenic, copper, boron, PAHs (Poly-Aromatic Hydrocarbons), BTEXs

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:23: PAHs are members of a large group of organic compounds widely distributed in the atmosphere. The best

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:23:known PAH is benzoapyrene (BaP). For the purpose of this assessment, Emissions of PAH have been assessed

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:23:against the AQAL set for benzo(a)pyrene as this is the only PAH which an AQAL has been set.

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:40:Aromatic Hydrocarbons network, which measures PAHs at 30 monitoring sites throughout the UK. This includes

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:40:in Table 19. The total PAH concentrations exceed the AQALs in all years presented.

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:40:Table 19: Measured annual mean PAH concentrations (ng/m3)

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:51:The maximum PC assuming all PAH emissions are B(a)P is 0.9% of the AQAL which is above the screening criteria

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:51:of 0.5%. Table 19 presents measured concentration of PAH. The maximum annual mean concentration for B(a)P

R-2019-0767-OOM-REP-1011778-AQ-CR-20200306-Grangetown Prairie Energy from Waste-AQA-R02.pdf:51:Table 34: Maximum Annual Mean PAH as B(a)P PEC at Relevant Exposure Location (ng/m3)

R-2020-0743-CD-Redcar - MPA Area Summary.pdf:5: metals, TPH, PAH, cyanides, phenols, VOC, Zinc

R-2020-0743-CD-Redcar - MPA Area Summary.pdf:5: PAHs

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:13: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:13: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:14: Metals (including heavy metals), PAH, cyanide,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:14: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:14:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:15:Concentrations of PAH were measured in 29 of the 32 soil samples analysed, and in all eight samples of soil

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:24:An exceedance of the EQS for five metals were recorded. Five PAH were measured in excess of DWS with

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:25:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:25:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:25:Concentrations of PAH have been measured in excess of WQS in the majority of leachate samples. Of the

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:25:measured concentrations of PAH in excess in leachate, the majority are considered to be marginally in excess

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:25:of the WQS. Given this, and that PAH are generally of low mobility in the natural environment, the risk to water

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:33:Metals (including heavy metals), PAHs, VOC,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:33:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:33:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:37:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part1.pdf:37:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:13: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:13: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:14: Metals (including heavy metals), PAH, cyanide,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:14: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:14:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:15:Concentrations of PAH were measured in 29 of the 32 soil samples analysed, and in all eight samples of soil

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:24:An exceedance of the EQS for five metals were recorded. Five PAH were measured in excess of DWS with

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:25:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:25:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:25:Concentrations of PAH have been measured in excess of WQS in the majority of leachate samples. Of the

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:25:measured concentrations of PAH in excess in leachate, the majority are considered to be marginally in excess

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:25:of the WQS. Given this, and that PAH are generally of low mobility in the natural environment, the risk to water

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:33:Metals (including heavy metals), PAHs, VOC,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:33:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:33:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:37:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:37:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:317: Sulphur (free) (7 days), Naphthalene (14 days), PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:318: Sulphur (free) (7 days), Naphthalene (14 days), PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:325: PAH is extracted from one litre of filtered water sample by

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:325: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:325: Note for PAH by SPE

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: dichloromethane (DCM) using sonication. The PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: concentration is recorded both as “Total PAH” and as

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: PAH concentration is recorded both as “Total PAH” and

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:344: 3302 1.6 mg/kg Total PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: The PAHs in the soil sample are extracted into hexane:

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils.pdf:345: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:36: Sulphur (free) (7 days), Naphthalene (14 days), PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:37: Sulphur (free) (7 days), Naphthalene (14 days), PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:44: PAH is extracted from one litre of filtered water sample by

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:44: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:44: Note for PAH by SPE

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: dichloromethane (DCM) using sonication. The PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: concentration is recorded both as “Total PAH” and as

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: PAH concentration is recorded both as “Total PAH” and

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:63: 3302 1.6 mg/kg Total PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: The PAHs in the soil sample are extracted into hexane:

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0125-02-MPA_Shallow_Soils_Part2.pdf:64: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0181-MPA_ROA and Strategy.pdf:40:Metals (including heavy metals), PAHs, VOC,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0181-MPA_ROA and Strategy.pdf:40:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0181-MPA_ROA and Strategy.pdf:40:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:17: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:17: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:18: Metals (including heavy metals), PAH, cyanide,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:18: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:18:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:19:Concentrations of PAH were measured in 2 of the 8 soil samples analysed, and in all four samples of soil

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:19:lower than those observed in Made Ground. Concentrations of asbestos, PAHs and TPH were all below the

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:20: PAH Total ug/l 0.82 < 0.80 0.48 < 0.20 0.58

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:20:levels just above the limit of detection. Concentrations of PAH did not indicate a decrease in water quality was

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:30:An exceedance of the EQS for seven metals and six PAH were recorded.

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:33:and PAHs were also measured in excess of WQS. It is noted that the groundwater pH is neutral to slightly

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:35:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:35:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:35:Concentrations of PAH have been measured in excess of WQS in ten leachate, six groundwater, and five

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:35:surface water samples. Of the measured concentrations of PAH in excess, they are considered to be

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:35:marginally in excess of the WQS. Given this, and that PAH are generally of low mobility in the natural

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:38:metals, ammoniacal nitrogen, PAH and phenol, that groundwater flow is potentially towards the River tees and

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:46:Metals (including heavy metals), PAHs, VOC,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:46:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:46:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:47:Metals (including heavy metals), PAHs, VOC,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:47:Metals (including heavy metals), PAHs,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:47:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0743-CD-10035117-AUK-XX-XX-RP-ZZ-0223-01-MPA_Deep_Soils.pdf:173: days), Nitrite as N (2 days), PAH MS (4 days)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:3: 3.6. Background Concentrations of NO2, VOC and PAH 68

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:5:Table 20: Long-term impacts of NO2, VOC and PAH – Step 2 Screening 73

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:6:Table 39: Long-term impacts of NO2, VOC and PAH – Step 2 Screening - Cumulative 137

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:7:Figure 32: PAH (as BaP) – Annual Mean – Met Year 2020 94

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:12: • PAH, as benzoapyrene (the AQS for PAH is expressed as benzoapyrene, and,

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:12: accordingly, for the purposes of the assessment, all PAH are assumed to be present

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:24: PAH (as

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:36: PAH (as benzoapyrene) 0.0001 0.0000422

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:69: PAH (as BaP) 75 2020 0.0000187 7.47%

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:71: • PAH (as BaP)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:77:3.5.5. The long-term impacts of NO2, VOC and PAH still requires further assessment. The next

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:77:3.6. Background Concentrations of NO2, VOC and PAH

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: PAH (as Benzoapyrene)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81:3.6.9. Monitoring of PAH has been undertaken by DEFRA since 1991. Currently, the network

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: consists of over 30 PAH measurement sites across England, Wales, Scotland and Northern

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: Ireland measuring ambient concentrations of PAH in UK atmosphere30.

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: The 2019 annual average PAH (as Benzoapyrene, solid phase) concentration at this

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: the PAH PECs.

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: long-term impacts of NO2, VOC and PAH. The criteria used to determine the significance of

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:82: Table 20: Long-term impacts of NO2, VOC and PAH – Step 2 Screening

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:82: PAH (as BaP) 95 2020 0.00000694 2.78% 0.000213 85% Slight

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:83: 110m. For PAH (as BaP) the impact on the environment can be classed as ‘slight’ for stack

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:83:3.9.2. The blue contour lines (as shown in Figures 13, 21 and 31 for annual NO2, VOC and PAH (as

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:11: Figure 32: PAH (as BaP) – Annual Mean – Met Year 2020

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:15: (as benzene) and 11 locations for PAH (as BaP). Consequently, PECs were considered for

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:15: sensitive human receptor locations were classed as ‘negligible’. For PAH (as BaP), the

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:17: Pollutant NH3 (annual) NH3 (1-hour) HCl (1 hour) HF (annual) HF (1-hour) PAH (as BaP) (annual) PCB (annual) PCB (1-hour) Dioxins & Furans (annual)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:46: PAH (as BaP)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:46: • PAH (as BaP)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:53:9.5.1. The long-term impacts of NO2, VOC and PAH, as displayed in Table 35, also require further

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:53: annual NO2, VOC and PAH is shown in Table 39, with any potentially significant PCs

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:54: Table 39: Long-term impacts of NO2, VOC and PAH – Step 2 Screening - Cumulative

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:54: PAH (as BaP)

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:55:9.5.4. For PAH (as BaP) the impact on the environment can be classed as ‘substantial’, in

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:55: annual GLC for PAH (as BaP) occurs in an area approximately 500m north of REC (456185

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:55: worst-case met year (i.e., NWP 2020) the annual GLC for PAH (as BaP) for REC was

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:55: PAH PCs, arising from four stacks modelled on a worst-case scenario basis (i.e., emitting at

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:55: considered necessary for annual NO2, VOC or PAH.

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:59: locations for VOC (as benzene) and all sixteen locations for PAH (as BaP). Consequently,

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:59: human receptor locations were classed as ‘negligible’. For PAH (as BaP), the human

R-2023-0224-CD-ECL.007.04.01_ADM - Issue 1a (2 of 3).pdf:61: NH3 NH3 (1- HCl (1 HF HF (1- PAH (as BaP) Dioxins & Furans

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Metals, ACMs, TPH, PAH, phenols, VOCs, SVOCs, herbicides.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: ACMs, TPH, PAH.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: TPH, PAH, VOCs, SVOCs.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Engine house (on-site and off-site) Metals, ACMs, TPH, PAH, phenols, VOCs, SVOCs.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Chimneys (on-site) TPH, PAH, VOCs, SVOCs.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Tanks / tank farm (on-site) TPH, PAH, VOCs, SVOCs.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: PAH, phenols, VOCs, SVOCs, BTEX, ACMs and ground gases.

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Metals, inorganics (fluoride, sulphates, phosphates), TPH, PAH, phenols,

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:17: Cyanide, metals, PAHs, coal tars, ammonium sulphate, ammonium

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:30: To further assess the risk from PCB and PAHs to future site commercial workers via the vapour

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:30: contaminant concentration in the vapour phase to that in the (pore) water phase. All PAHs and PCBs

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:35: Exceedances of the GACs for metals, cyanide, PAH and TPH were

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:35: Contaminants TPH, PAH,

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:37: Contaminants in exceedance of the GAC for human health at the site are limited to PAHs and dibenzofuran from one location in

R-2023-0247-OOM-TV_BAF_Contaminated_Land_Review.pdf:44: cyanide and selected PAHs (NAPL) in shallow soils across Grangetown Prairie; and

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:21: metals, pH, sulphate cyanide and PAHs, phenol,

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:21: pH, sulphate, cyanide and PAHs, phenol and TPH

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:27: levels of PAHs in the shallow soils, which are most likely as a result of localised spillages.

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:28:G4.65 Concentrations of PAH were measured in almost all the samples of slag dominant material and

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:28: PAH compounds (low levels) were recorded.

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:32: concentrations of metals, TPH and PAH compounds (low levels) were recorded above the Water

R-2020-0820-ESM-Lackenby ES - Vol 2 - Chapter G Ground Conditions - Dec 2020.PDF:40: 16 PAH Polycyclic Aromatic Hydrocarbons

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:16: bottles (for TPH, and PAH) and 40ml glass vials (for VOCs).

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:16: glass bottles (for TPH, and PAH) and 40ml glass vials (for VOCs).

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:22: 16 ü sulphates and PAH’s

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:28: Elevated levels of Total PAH were detected in only one sample (184 mg/kg –

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:28: 11AT4A, 0.3 m bgl). The 95 percentile calculated for Total PAH (18 mg/kg)

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:29:DIV 40 mg/kg PAH Total EPA16 17.91 <16 <16 <16 <16 <184 <16 <18 <18 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:30:DIV 40 mg/kg PAH Total EPA16 17.91 <16 <16 <16 <16 <16 <28

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:32: Elevated levels of Total PAH were detected in six samples (12AT8, 2.0m bgl;

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:32: and, 12AT17, 0.3m bgl). PAH values exceeding guideline values range from

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:32: percentile calculated for Total PAH (31 mg/kg) is below the guideline value of

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:33:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <120 <16 <16 <100 <41 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:34:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <56 <16 <16 <16 <16 <17 <16 <22 <50

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:35:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <16 <16 <16 <16 <17 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:36:DIV 40 mg/kg PAH Total EPA16 30.80 <16 <309 <22 <18 <26 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:38: Elevated levels of Total PAH were detected in two locations (47 mg/kg –

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:38: calculated for Total PAH (19.5 mg/kg) was well below the guideline value of 40

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:39:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:40:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16 <16 <16 <16 <18 <47 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:41:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <38 <16 <26 <16 <16 <16 <16 <16 <153

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:42:DIV 40 mg/kg PAH Total EPA16 19.56 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:44: Slightly elevated levels of Total PAH were detected at three locations (4 2

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:44: 4.0 m bgl). The 95 percentile calculated for Total PAH (26.07 mg/kg) was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:45:DIV 40 mg/kg PAH Total EPA16 26.07 <42 <16 <16 <16 <44 <16 <27 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:46:DIV 40 mg/kg PAH Total EPA16 26.07 <16 <16 <16 <68 <18 <16 <32 <34

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:49: Elevated levels of Total PAH were detected in five samples (48 mg/kg –

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:49: The 95th percentile calculated for Total PAH (19.5 mg/kg) across the whole of

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:50:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <32 <16 <28 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:51:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <17 <38.45 <16 <16 <17 <16 <31 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:52:DIV 40 mg/kg PAH Total EPA16 19.45 <48 <16 <96 <20 <16.07 <16 <20.88 <16 <16 <19.97

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:53:DIV 40 mg/kg PAH Total EPA16 19.45 <19.87 <40.82 <18.6 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:54:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:55:DIV 40 mg/kg PAH Total EPA16 19.45 <16 <16 <16 <16 <16 <52 <16 <23 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:56:DIV 40 mg/kg PAH Total EPA16 19.45 <20 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:59:DIV 40 mg/kg PAH Total EPA16 <16 <31 <16 <27 <27 <16 <16 <29 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:61: Elevated levels of Total PAH were detected in seven samples across the area,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:61: (17AT5, 4.0 m bgl). The 95 percentile calculated for Total PAH across Area

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:62:DIV 40 mg/kg PAH Total EPA16 28.28 <19 <16 <16 <17 <25 <74 <16 <16 77.0 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:63:DIV 40 mg/kg PAH Total EPA16 28.28 <43 <16 <16 <16 <18 <21 <23 <16 <16 <422

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:64:DIV 40 mg/kg PAH Total EPA16 28.28 <25 <16 <16 <32 <16 <35 <25 <104 <16 <28

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:65:DIV 40 mg/kg PAH Total EPA16 28.28 <21 <16 <39 <16 <19 <16 <16 <17 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:66:DIV 40 mg/kg PAH Total EPA16 28.28 <16 <16 342.0 298.0 <18

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:68:DIV 0.82 mg/l PAH Total EPA16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:68:NB. DIV for PAH is for sum of ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:72:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:72:NB. DIV for PAH is for sum of ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:73:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:73:NB. DIV for PAH is for sum of ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:75: • PAH’s were elevated in the ground at shallow and deep samples primarily in

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:77: phenols, sulphates and PAH’s

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:81: In Area 7, elevated levels of Total PAH were detected in only one sample

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:81: (7AT1, 1.5m bgl – 51 mg/kg). The 95 percentile calculated for Total PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:82:DIV 40 mg/kg PAH Total EPA16 18.10 <16 <16 <51 <31 <16 <16 <17 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:83:DIV 40 mg/kg PAH Total EPA16 18.10 <18 <17 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:85: Elevated levels of Total PAH were detected in only one sample (377 mg/kg –

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:85: 8AT3, 0.2 m bgl). The 95 percentile calculated for Total PAH (18 mg/kg) was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:86:DIV 40 mg/kg PAH Total EPA16 17.58 <16 <16 <16 <24 <377 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:88: Elevated levels of Total PAH were detected in two locations (169 mg/kg –

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:88: for Total PAH (29 mg/kg) was below the guideline value of 40 mg/kg.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:89:DIV 40 mg/kg PAH Total EPA16 28.75 <16 <16 <169 <61

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:93:DIV 0.82 mg/l PAH Total EPA16 0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <0.16 <5

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:93:NB. DIV for PAH is for sum of ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:95: apart from isolated levels of PAHs in the shallow soils, which are most likely as

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:97: H ü contain metals, phenols, sulphates and PAH’s

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:102: Levels of Total PAH in excess of guideline criteria were detected in seven

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:102: bgl). The 95th percentile calculated for Total PAH (43.69 mg/kg) exceeds the

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:103:DIV 40 mg/kg PAH Total EPA16 43.69 <40 <20 <100 <16 <20 <19 <19 <16 <21 <50

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:104:DIV 40 mg/kg PAH Total EPA16 43.69 <21 <61 <37 <20 85.0 <21 <16 <16 <61 139.0

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:105:DIV 40 mg/kg PAH Total EPA16 43.69 <77 <16 <18 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:107: Levels of Total PAH in excess of guideline values were detected in fifteen

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:107: m bgl). The 95th percentile calculated for Total PAH (2,167 mg/kg) across all

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:108:DIV 40 mg/kg PAH Total EPA16 2167.24 <7043 <166 20780.0 <47 <16 <72 <17 <18 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:109:DIV 40 mg/kg PAH Total EPA16 2167.24 <34 <16 <327 <18 <81 <62 <75 <39 418.0 <23

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:110:DIV 40 mg/kg PAH Total EPA16 2167.24 4196.0 <16 658.0 145483.0 <87 <16 <50 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:112: Elevated levels of Total PAH in excess of guideline criteria were detected in

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:112: 4 6 m g / k g (3AT6 (3.5 m bgl). The 95th percentile calculated for Total PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:113:DIV 40 mg/kg PAH Total EPA16 43.41 <16 <400 <18 <17 <16 <16 <89 <18 <46 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:115: Levels of Total PAH in excess of guideline criteria were detected in five

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:115: percentil e calculated for Total PAH (236.76 mg/kg) across A r e a 4 exceeded

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:116:DIV 40 mg/kg PAH Total EPA16 236.76 <16 <389 <17 <465 <47 179.0 <16 <17 <470 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:118: Elevated levels of PAH were observed in five samples across Area D ranging

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:119:DIV 40 mg/kg PAH Total EPA16 19.07 <34 <18 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:120:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 <38 <16 <16 <16 <20

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:121:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 120.0 <19 <16 <16 <17

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:122:DIV 40 mg/kg PAH Total EPA16 19.07 <18 <16 <16 <18 <16 <23 <16 <18 <16 <58

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:123:DIV 40 mg/kg PAH Total EPA16 19.07 <20 103.0 <16 <19 <16 <19 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:124:DIV 40 mg/kg PAH Total EPA16 19.07 <18 <49 <16 <16 <16 <16 <16 <16 <18 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:125:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:126:DIV 40 mg/kg PAH Total EPA16 19.07 <16 <16 <16 <16 <45 <36 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:129: Levels of Total PAH in excess of guideline values were detected in ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:129: levels of Total PAH ranging from 41 mg/kg (ECT41, 0.6m bgl) to 209 mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:129: In sub-A rea D there were six samples with elevated levels of Total PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:130:DIV 40 mg/kg PAH Total EPA16 25.30 <26 <40 <20 <16 <16 <32 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:131:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <16 <16 <16 <17 <16 <16 <18 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:132:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <40 <18 <16 <16 <16 <16 <16 <37 <60

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:133:DIV 40 mg/kg PAH Total EPA16 25.30 <18 <16 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:134:DIV 40 mg/kg PAH Total EPA16 25.30 <77 <209 <16 <41 <26 <26 <18 <16 <18 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:135:DIV 40 mg/kg PAH Total EPA16 25.30 <22 <29 <18 <16 <30 241.0 237.0 <55 <17 <37

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:136:DIV 40 mg/kg PAH Total EPA16 25.30 <52 <29 <16 <16 <16 <16 <16 <16 <16 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:137:DIV 40 mg/kg PAH Total EPA16 25.30 <16 <16 <48 <17 <16 <76 <18

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:140:DIV 40 mg/kg PAH Total EPA16 36.00 <16 <36 <39 <16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:142: Five groundwater samples contained PAHs in concentrations exceeding the

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:142: 95 percentile calculated for PAHs of 2.95 mg/l exceeds the guideline value of

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:143:DIV 0.8 mg/l PAH Total EPA16 2.95 <83.55 <0.21 <0.18 <7.11 <1.67 <0.17 <4.34 <0.33 <0.16 1.5 <0.16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:143:NB. DIV for PAH is for sum of ten

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:145: • Hydrocarbons including PAHs, BTEX Compounds and TPH were identified in

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:148: • Locally elevated PAH levels in excess of guideline criteria were found

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:148: • The bulk oil tank s near the Blast Furnace; Elevated PAHs and BTEX occurred

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:148: • The SLEMS area; PAHs, and BTEX exceeded the Tier 1 soil screening criteria

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:148: groundwater samples were in excess of screening values for BTEX, PAH, GRO

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:149: PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:149: PAH Polyaromatic Hydrocarbons

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:165: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:167: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:169: SO Zn D-A-T11 D B SO SO 3-A-B2 PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:175: PA PAH Total EPA16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:185: criteria. PAH concentrations were also elevated in soils from the eastern area of 12

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:191: from isolated levels of PAHs in the shallow soils, which are most likely as a result

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:195: Elevated concentrations of PAH, BTEX compounds and, to a lesser degree TPH,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:199: contaminants (TPH, PAH and BTEX Compounds 8 ). The occurrence of elevated

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:199:8 TPH – Total Petroleum Hydrocarbons; PAH- Poly Aromatic Hydrocarbons; BTEX Compounds – Benzene,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:207: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:213: PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:219: SO Zn D-A-T11 D B SO SO 3-A-B2 PA PAH Total EPA16 DIV 40mg/kg

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:221: PA PAH Total EPA16

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:231:storage and use hydraulic fluid, ingestion, inhalation Medium E levated soil PAH in nort h and eastern portions of the area, Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:235:s t o r a g e a nd hydraulic fluid, ingestion, inhalation Medium Slightly elevated levels of PAH detected in soils, and elevated TPH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:235: Mild migration. Elevated levels of TPH and PAH identified in soil and

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:241: Mild migration. Limited elevated levels of metals and PAH i n

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:241: and gravel Mild underlying sands. Limited elevated levels of metals and PAH in

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:245:use greases and solvents utilised. Elevated PAH detected in one soil samples, although

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:245: permeable strata Mild migration. Limited elevated soil PAH detected, however no

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:247: phytotoxic and heavy utilised. Elevated levels of PAHs detected at two locations.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:247:use greases and solvents utilised. Elevated levels of PAHs detected at two locations .

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:250: creosote, tar, ingestion, inhalation Medium Locally elevated soil PAH in shallow and deep soil , source not

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:250: permeable strata Mild migration. Locally elevated soil PAH in shallow and deep soil,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:252: creosote, tar, ingestion, inhalation Medium Locally elevated s o i l PAHs and BTEX compounds at eastern side of Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:252: (River Tees) permeable strata water Locally elevated soil PAHs and BTEX compounds at east ern side of Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:253: (Estuarine and permeable strata groundwater Locally elevated soil PAHs and BTEX compounds at eastern side of

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:253: Marine Alluvium Mild site. Similarly elevated hydrocarbons in groundwater; PAHs, BTEX,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:253: receptors (Tees drainage or sensitive SSSI E levated hydrocarbons in groundwater; PAHs, BTEX, GRO, TPH.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:257:(Area 2) creosote, tar, ingestion, inhalation Medium Locally elevated soil PAHs and BTEX compounds in soil. Site Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:257: (River Tees) permeable strata water Locally elevated soil PAHs and BTEX in soil . Open areas allow Low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:258: (Estuarine and permeable strata groundwater Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:258: receptors (Tees drainage or s e n s i t iv e S S S I Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:258: (i.e. land which drainage or adjacent land values Locally elevated soil PAHs and BTEX compounds and slightly

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:259:storage and hydraulic fluid, ingestion, inhalation Medium Locally elevated soil PAHs and BTEX compounds in soil. Site

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:259: (River Tees) permeable strata water Locally elev a t e d soil PAHs and BTEX in soil . Open areas allow

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:265:work was 15th June, allowing a 13-week programme. zinc, boron; organics - TPH, PAH and BTEX compounds3.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:265:3 TPH: Total Petroleum Hydrocarbons; PAH: Poly-Aromatic Hydrocarbons: BTEX Compounds; Benzene, Toluene, Ethyl-benzene and Xylene.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:266:Elevated concentrations of PAH, BTEX compounds and, to a workers engaged in excavation

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:268:Lackenby Works apart from isolated levels of PAHs in the Receptors pathway is direct however

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:271:and boron, were found in excess of screening criteria. PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1358: Naphthalene, PAH MS

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1372: days), PAH MS (14 days), pH +

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1377: PAH is extracted from one litre of filtered water sample by

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1377: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1377: Note for PAH by SPE

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: dichloromethane (DCM) using sonication. The PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: concentration is recorded both as “Total PAH” and as

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: PAH concentration is recorded both as “Total PAH” and

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1396: 3302 1.6 mg/kg Total PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: The PAHs in the soil sample are extracted into hexane:

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1397: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1408: PAH Glass 20g EPA Victoria 14 days -

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1409: PAH Glass 500 CIP 2 Tech Spec none 5 days

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1434:TPB28 1.5m (the concentration was 11x EQS). The same five PAHs were detected above DWS in Area B,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1436:in Area A exceeded WQS screening criteria for copper and manganese, and several PAH compounds.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1436:sediment suspension as samples were filtered on the second monitoring round. The TPH and PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1440:Several PAH compounds do not have WQS, but these will be adequately covered under recommendations for

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1440:the PAH compounds identified as exceeding their applicable WQS. PAH compounds are generally of low

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1440:Low levels of dissolved petroleum hydrocarbons, including PAHs have been detected in shallow groundwater

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1469: PAHs

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1469: PAH - USEPA 16, Total 0.1 mg/kg None 330 71

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1475: PAHs

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1475: PAH Total 0.04 ug/l 85 0.61

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1478: PAH Total na

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1480: PAHs

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1480: PAH Total 0.04 ug/l 4.5 100

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1511: Railway lines and sidings Metals, asbestos, TPH, PAH, sulphate, sulphide, and pH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1511: metals), asbestos, PAHs, volatile organic compounds

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1511: Above Ground Storage tanks (various) TPH, PAH, including metals, hydrocarbons, pH.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1512: Metals, asbestos, TPH, PAH, VOCs, SVOCs, chloride,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1512: B but considered off site for this review. Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1512: Locomotive Repair Shop Metals, asbestos, PAHs, VOC, SVOC, and pH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1512: Metals, asbestos, TPH, PAH, VOC, SVOC, cyanides,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1512:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515:Concentrations of PAH were measured in all the samples of slag dominant material, all but one of the granular

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515:chains, rods, and wire had been identified in the trial pit, showed levels of PAH comparable to the other Made

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515:Leached concentrations of PAH were measured in all three samples analysed, leached concentrations ranged

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515:Elevated concentrations of PAH (330mg/kg and 100mg/kg) and similar levels of TPH were measured in S3-

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: • An elevated concentration of TPH (560mg/kg) was measured in S3-TPA21 (0.5m bgl), PAH levels

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: • An elevated concentration of TPH (640mg/kg) was measured in S3-TPA26 (0.2m bgl), PAH levels

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: leaching tests on the sample, low levels of PAH were noted to leach. The low leachability and solubility

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: • An elevated concentration of TPH (1,800mg/kg) was measured in S3-TPA32 (1m bgl), PAH levels

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: • An elevated concentration of TPH (640mg/kg) was measured in S3-TPA39 (0.3m bgl), elevated PAH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: screening. A concentration of 58µg/l TPH and 58µg/l PAH was measured following leaching tests on

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1515: • An elevated concentration of TPH (900mg/kg) was measured in S3-TPA42 (0.2m bgl), PAH levels

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1516: of PAH were measured in leachate but these were only marginally above the MDL. The low leachability

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1516:elevated TPH and PAH are shown on Figure 10 below and in Appendix X.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1516:notably elevated compared to other samples. Concentrations of two PAHs were measured just above the MDL

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1517:Levels of PAH were also measured in groundwater sampled from both monitoring wells, concentrations were

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1521: • Steelmaking areas Metals, asbestos, PAH, VOC, SVOC, cyanide,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1521: Railway lines and sidings Metals, asbestos, TPH, PAH, sulphate, sulphide, and pH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1521: Grangetown Power Station Metals, asbestos, TPH, PAH, PCBs, sulphate

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522: Metals, asbestos, TPH, PAH, VOCs, SVOCs, chloride,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522: Torpedo Ladle Repair Shop – Part of SSI3 Area A but Metals, asbestos, PAHs, volatile organic compounds

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522: Locomotive Repair Shop Metals, asbestos, PAHs, VOC, SVOC, and pH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522: Metals, asbestos, TPH, PAH, VOC, SVOC, cyanides,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1522:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525:Concentrations of PAH were measured in almost all the samples of slag dominant material and granular made

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525:and wood had been identified in the trial pit, showed levels of PAH comparable to the other Made Ground

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525:Leached concentrations of PAH were measured all six samples and comprised a broad range of light to heavy

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: - 1.9m bgl) located within the area of former slag pits, concentrations of PAH within the same samples

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: to the clarifiers, concentrations of PAH in the same sample were 26mg/kg. No visual or olfactory

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: the storage area south east of the BOS building, concentrations of PAH within the same sample was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: 1.7µg/l TPH and 0.3µg/l PAH was measured following leaching tests on the sample, the results

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:1525: the contamination was mid-range to heavy end hydrocarbons. A concentration 0.61µg/l PAH was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1525: west of the water treatment plan and slag transporter workshop, concentrations of PAH within the

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1526: concentration of 2.7µg/l TPH and 0.44µg/l PAH was measured following leaching tests on the sample,

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:1526: A concentration 0.01µg/l PAH was measured following leaching tests on the sample, no TPH was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1526: south of the site close to a small stores building, concentrations of PAH within the same sample was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1528:particularly for chromium, lead, and zinc. Concentrations of PAHs were measured marginally above the MDL

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1528:Concentrations of PAH were generally low <5µg/l with the exception of S3-BHB04s/d during the first sampling

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1533: • Based on a statistical analysis the highest concentrations of metals and PAH were generally identified

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1533: • Tests identified that metals readily leached from Made Ground deposits, TPH and PAH were also

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1533: noted to leach in some samples. Metals, TPH and PAH were also detected in groundwater at both

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1574: PAH - USEPA 16, Total 36/36 150 1 19.481 33.162

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1575: Total PAH 9/9 330 0.79 39.232 102.828

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1576: Total PAH 3/3 0.5 0.5 10.567 13.744

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1578: PAH - USEPA 16, Total 31/31 26 0.11 3.254 5.212

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1579: Total PAH 45/45 71 0.26 6.998 15.105

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1580: Total PAH 12/12 3.5 0.05 0.600 0.910

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1666: PAHS.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1683:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1683: PAHs, phenol and TPH. Were taken from within the site boundary

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1683: sulphate cyanide and PAHs, phenol and TPH

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1684: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1684: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1698:  Railway ballast containing metals and PAHs,

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1698: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1699: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1699: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1700: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1700: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1701: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1701: exception of PAH results.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1701: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1701: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1702: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1713: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1713: westerly direction (towards the Tees). The pH was alkaline. TPH and PAHs were below detection, but copper

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1714: Analysis of soil samples did not show concentration for metals, PAHs and TPH above Commercial GACs.

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1714: westerly direction (towards the Tees) The pH was alkaline. TPH and PAHs were below detection limits, but

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1734: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1734:  PAHs – 1 sample (GAC 40mg/kg)

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1744: hydrocarbons, PAHs and BT

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1749:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s, VOCs, SVOCs and aromatic

R-2020-0820-ESM-Lackenby ES - Vol 3 - Chapter G - Ground Conditions - Dec 2020.pdf:1749:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:6:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:8: PAHS.

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: PAHs, phenol and TPH. Were taken from within the site boundary

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: sulphate cyanide and PAHs, phenol and TPH

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43:  Railway ballast containing metals and PAHs,

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: exception of PAH results.

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:47: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83:  PAHs – 1 sample (GAC 40mg/kg)

R-2020-0270-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:93: hydrocarbons, PAHs and BT

R-2021-0432-FFM-10035117-AUK-XX-XX-SP-ZZ-0258-P1-Water Treatment Prairie Excavations -Se....pdf:3:Total PAH’s max 5 mg/l

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1065: Naphthalene, PAH MS

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1079: days), PAH MS (14 days), pH +

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1084: PAH is extracted from one litre of filtered water sample by

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1084: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1084: Note for PAH by SPE

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: dichloromethane (DCM) using sonication. The PAH

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: concentration is recorded both as “Total PAH” and as

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: PAH concentration is recorded both as “Total PAH” and

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1103: 3302 1.6 mg/kg Total PAH

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: The PAHs in the soil sample are extracted into hexane:

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1104: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1115: PAH Glass 20g EPA Victoria 14 days -

R-2021-0432-FFM-4155 The Former SSI Steelworks, Redcar - Contract 3 (Final Report).PDF:1116: PAH Glass 500 CIP 2 Tech Spec none 5 days

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:26: Railway lines and sidings Metals, asbestos, TPH, PAH, sulphate, sulphide, and pH

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:26: metals), asbestos, PAHs, volatile organic compounds

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:26: Above Ground Storage tanks (various) TPH, PAH, including metals, hydrocarbons, pH.

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:27: Metals, asbestos, TPH, PAH, VOCs, SVOCs, chloride,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:27: B but considered off site for this review. Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:27: Locomotive Repair Shop Metals, asbestos, PAHs, VOC, SVOC, and pH

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:27: Metals, asbestos, TPH, PAH, VOC, SVOC, cyanides,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:27:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30:Concentrations of PAH were measured in all the samples of slag dominant material, all but one of the granular

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30:chains, rods, and wire had been identified in the trial pit, showed levels of PAH comparable to the other Made

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30:Leached concentrations of PAH were measured in all three samples analysed, leached concentrations ranged

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30:Elevated concentrations of PAH (330mg/kg and 100mg/kg) and similar levels of TPH were measured in S3-

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: • An elevated concentration of TPH (560mg/kg) was measured in S3-TPA21 (0.5m bgl), PAH levels

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: • An elevated concentration of TPH (640mg/kg) was measured in S3-TPA26 (0.2m bgl), PAH levels

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: leaching tests on the sample, low levels of PAH were noted to leach. The low leachability and solubility

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: • An elevated concentration of TPH (1,800mg/kg) was measured in S3-TPA32 (1m bgl), PAH levels

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: • An elevated concentration of TPH (640mg/kg) was measured in S3-TPA39 (0.3m bgl), elevated PAH

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: screening. A concentration of 58µg/l TPH and 58µg/l PAH was measured following leaching tests on

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:30: • An elevated concentration of TPH (900mg/kg) was measured in S3-TPA42 (0.2m bgl), PAH levels

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:31: of PAH were measured in leachate but these were only marginally above the MDL. The low leachability

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:31:elevated TPH and PAH are shown on Figure 10 below and in Appendix X.

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:31:notably elevated compared to other samples. Concentrations of two PAHs were measured just above the MDL

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:32:Levels of PAH were also measured in groundwater sampled from both monitoring wells, concentrations were

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:36: • Steelmaking areas Metals, asbestos, PAH, VOC, SVOC, cyanide,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:36: Railway lines and sidings Metals, asbestos, TPH, PAH, sulphate, sulphide, and pH

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:36: Grangetown Power Station Metals, asbestos, TPH, PAH, PCBs, sulphate

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37: Metals, asbestos, TPH, PAH, VOCs, SVOCs, chloride,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37: Torpedo Ladle Repair Shop – Part of SSI3 Area A but Metals, asbestos, PAHs, volatile organic compounds

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37: Locomotive Repair Shop Metals, asbestos, PAHs, VOC, SVOC, and pH

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37: Metals, asbestos, TPH, PAH, VOC, SVOC, cyanides,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:37:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40:Concentrations of PAH were measured in almost all the samples of slag dominant material and granular made

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40:and wood had been identified in the trial pit, showed levels of PAH comparable to the other Made Ground

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40:Leached concentrations of PAH were measured all six samples and comprised a broad range of light to heavy

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: - 1.9m bgl) located within the area of former slag pits, concentrations of PAH within the same samples

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: to the clarifiers, concentrations of PAH in the same sample were 26mg/kg. No visual or olfactory

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: the storage area south east of the BOS building, concentrations of PAH within the same sample was

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: 1.7µg/l TPH and 0.3µg/l PAH was measured following leaching tests on the sample, the results

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: to water treatment plant, concentrations of PAH within the same sample was 27mg/kg. A tar like

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: the contamination was mid-range to heavy end hydrocarbons. A concentration 0.61µg/l PAH was

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:40: west of the water treatment plan and slag transporter workshop, concentrations of PAH within the

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:41: concentration of 2.7µg/l TPH and 0.44µg/l PAH was measured following leaching tests on the sample,

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:41: south-east of the site, concentration of PAH within the same sample was 4.2mg/kg. A tar like

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:41: A concentration 0.01µg/l PAH was measured following leaching tests on the sample, no TPH was

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:41: south of the site close to a small stores building, concentrations of PAH within the same sample was

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:43:particularly for chromium, lead, and zinc. Concentrations of PAHs were measured marginally above the MDL

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:43:Concentrations of PAH were generally low <5µg/l with the exception of S3-BHB04s/d during the first sampling

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:48: • Based on a statistical analysis the highest concentrations of metals and PAH were generally identified

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:48: • Tests identified that metals readily leached from Made Ground deposits, TPH and PAH were also

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:48: noted to leach in some samples. Metals, TPH and PAH were also detected in groundwater at both

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:89: PAH - USEPA 16, Total 36/36 150 1 19.481 33.162

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:90: Total PAH 9/9 330 0.79 39.232 102.828

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:91: Total PAH 3/3 0.5 0.5 10.567 13.744

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:93: PAH - USEPA 16, Total 31/31 26 0.11 3.254 5.212

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:94: Total PAH 45/45 71 0.26 6.998 15.105

R-2021-0432-FFM-Redcar Steelworks-AUK-XX-XX-RP-GE-0001-02-SSI3_GI_SCR.PDF:95: Total PAH 12/12 3.5 0.05 0.600 0.910

R-2023-0339-CD-230328 JER10061 Redcar Energy Centre LPA Letter Final Rev 2.pdf:17: determinants, TPH’s, PAH’s and asbestos identification screening.

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:13: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:benzene, dibenzofuran, and PAHs that were measured in excess of the Generic Assessment Criteria

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:22: from materials impacted with Lead, arsenic, asbestos, cyanide, and PAHs; and,

R-2022-0355-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:41:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0846-FFM-Arcadis - South Bank Strategy.pdf:10: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: PAH is extracted from one litre of filtered water sample by

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: Note for PAH by SPE

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: dichloromethane (DCM) using sonication. The PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: concentration is recorded both as “Total PAH” and as

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: PAH concentration is recorded both as “Total PAH” and

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: 3302 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: The PAHs in the soil sample are extracted into hexane:

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: PAH is extracted from one litre of filtered water sample by

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: Note for PAH by SPE

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: dichloromethane (DCM) using sonication. The PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: concentration is recorded both as “Total PAH” and as

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: PAH concentration is recorded both as “Total PAH” and

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: 3302 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: The PAHs in the soil sample are extracted into hexane:

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:55: Total PAH 14 2600 0.05 254 652

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:56: Total PAH 70 110000 0.05 1722 12974

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:57: Total PAH 5 14 0.49 4.26 4.97

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:58: USEPA 16 PAH 6 1700 0.05 214 562

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: PAH is extracted from one litre of filtered water sample by

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: Note for PAH by SPE

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: dichloromethane (DCM) using sonication. The PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: concentration is recorded both as “Total PAH” and as

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: PAH concentration is recorded both as “Total PAH” and

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: 3302 1.6 mg/kg Total PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: The PAHs in the soil sample are extracted into hexane:

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:12:Concentrations of PAH were measured in 4 of the 5 samples analysed and concentrations of TPH were

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:Low levels of PAH were measured in the majority of samples with higher concentrations recorded in

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:22:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:22:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: including tars, PAH, cyanides, thiocyanate, volatile

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Railways and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, and pH.

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Above Ground Storage tanks (various) TPH, PAH, pH.

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, VOC, SVOC,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, TPH, PAHs, VOC, SVOC, cyanide, thiocyanate,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Water resources – Metals, ammoniacal nitrogen and PAH

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:26:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:Concentrations of PAH were measured in 90 of the 101 samples analysed. Statistical analysis indicates that,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:within granular made ground, PAH concentrations were an order of magnitude higher than within slag dominant

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:Made Ground. Concentrations of PAH measured in cohesive Made Ground were a further order of magnitude

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:30:Leached concentrations of PAH were measured in all samples analysed and comprised a broad range of both

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:32:Where PAHs or TPH were detected they were generally measured only marginally above the MDL with the

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:40:The concentrations measured by third parties in excess of the GAC were all PAHs and are in line with the

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:42:of PCBs, PAHs and carbazole in soil via the vapour inhalation pathway – driven by vapour intrusion (pollutant

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:48:Concentrations of heavy metals, ammoniacal nitrogen, TPH, PAH and phenol were measured in excess of

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:Concentrations of manganese and PAHs have been measured in excess of WQS in more than half of the

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:of their MDL: magnesium, sulphate, sulphur, chloride, free cyanide, thiocyanate, selected PAHs, styrene,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:53:screening the Made Ground and the superficial deposits. The highest concentrations of TPH, PAH and VOCs

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:56:including slag materials) and groundwater were assessed using GAC. Concentrations of arsenic and PAHs

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:56:Concentrations of arsenic, total cyanide and PAHs will need to be considered in the remedial strategy for the

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:2:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:3: PAH (ex. Naphthalene)

R-2020-0730-CD-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:4:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0439-CD-South Bank Quay Strategy Rev. 1.pdf:20: from materials impacted with arsenic, asbestos and PAHs; and,

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:3: 3.6. Background Concentrations of NO2, VOC and PAH 68

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:5:Table 20: Long-term impacts of NO2, VOC and PAH – Step 2 Screening 73

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:6:Table 39: Long-term impacts of NO2, VOC and PAH – Step 2 Screening - Cumulative 137

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:7:Figure 32: PAH (as BaP) – Annual Mean – Met Year 2020 94

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:12: • PAH, as benzoapyrene (the AQS for PAH is expressed as benzoapyrene, and,

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:12: accordingly, for the purposes of the assessment, all PAH are assumed to be present

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:24: PAH (as

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:36: PAH (as benzoapyrene) 0.0001 0.0000422

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:69: PAH (as BaP) 75 2020 0.0000187 7.47%

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:71: • PAH (as BaP)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:77:3.5.5. The long-term impacts of NO2, VOC and PAH still requires further assessment. The next

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:77:3.6. Background Concentrations of NO2, VOC and PAH

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: PAH (as Benzoapyrene)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81:3.6.9. Monitoring of PAH has been undertaken by DEFRA since 1991. Currently, the network

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: consists of over 30 PAH measurement sites across England, Wales, Scotland and Northern

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: Ireland measuring ambient concentrations of PAH in UK atmosphere30.

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: The 2019 annual average PAH (as Benzoapyrene, solid phase) concentration at this

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: the PAH PECs.

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:81: long-term impacts of NO2, VOC and PAH. The criteria used to determine the significance of

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:82: Table 20: Long-term impacts of NO2, VOC and PAH – Step 2 Screening

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:82: PAH (as BaP) 95 2020 0.00000694 2.78% 0.000213 85% Slight

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:83: 110m. For PAH (as BaP) the impact on the environment can be classed as ‘slight’ for stack

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:83:3.9.2. The blue contour lines (as shown in Figures 13, 21 and 31 for annual NO2, VOC and PAH (as

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:103: Figure 32: PAH (as BaP) – Annual Mean – Met Year 2020

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:107: (as benzene) and 11 locations for PAH (as BaP). Consequently, PECs were considered for

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:107: sensitive human receptor locations were classed as ‘negligible’. For PAH (as BaP), the

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:109: Pollutant NH3 (annual) NH3 (1-hour) HCl (1 hour) HF (annual) HF (1-hour) PAH (as BaP) (annual) PCB (annual) PCB (1-hour) Dioxins & Furans (annual)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:138: PAH (as BaP)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:138: • PAH (as BaP)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:145:9.5.1. The long-term impacts of NO2, VOC and PAH, as displayed in Table 35, also require further

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:145: annual NO2, VOC and PAH is shown in Table 39, with any potentially significant PCs

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:146: Table 39: Long-term impacts of NO2, VOC and PAH – Step 2 Screening - Cumulative

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:146: PAH (as BaP)

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:147:9.5.4. For PAH (as BaP) the impact on the environment can be classed as ‘substantial’, in

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:147: annual GLC for PAH (as BaP) occurs in an area approximately 500m north of REC (456185

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:147: worst-case met year (i.e., NWP 2020) the annual GLC for PAH (as BaP) for REC was

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:147: PAH PCs, arising from four stacks modelled on a worst-case scenario basis (i.e., emitting at

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:147: considered necessary for annual NO2, VOC or PAH.

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:151: locations for VOC (as benzene) and all sixteen locations for PAH (as BaP). Consequently,

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:151: human receptor locations were classed as ‘negligible’. For PAH (as BaP), the human

R-2023-0253-RMM-ECL.007.04.01_ADM - Issue 1a (1 of 3).pdf:153: NH3 NH3 (1- HCl (1 HF HF (1- PAH (as BaP) Dioxins & Furans

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:44: levels in excess of screening levels for metals, PAH’s and TPH.

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:45: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001_CEMP_A (Fit for Construction)_C03.pdf:45: PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:44: levels in excess of screening levels for metals, PAH’s and TPH.

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:45: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2021-0943-CD-SBQ1-GCL-ENV-SBKXX-PL-WM-000001.pdf:45: PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:12:for human health. Concentrations of arsenic, total cyanide and PAHs were measured above their respective

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:12:Multiple CoC including metals, total cyanide, ammoniacal nitrogen, TPH, PAH, phenol, xylene and 1,2-

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:20:Holme Beck were generally less than the applicable EQS with the exception of two PAH compounds which

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:24:heavy metals, inorganic compounds and PAHs have been identified in the subsurface at concentrations which

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:24:such as PAHs, including naphthalene. A number of options for the remediation of this gross contamination

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0088-01-Prairie_Risk Assessment (1).pdf:26:measured in Holme Beck were generally less than the applicable EQS with the exception of two PAH

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:12:Concentrations of PAH were measured in 4 of the 5 samples analysed and concentrations of TPH were

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:13:Low levels of PAH were measured in the majority of samples with higher concentrations recorded in

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:22:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:22:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: PAH is extracted from one litre of filtered water sample by

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1348: Note for PAH by SPE

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: dichloromethane (DCM) using sonication. The PAH

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: concentration is recorded both as “Total PAH” and as

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Hydrocarbons 1.6 mg/kg Total PAH

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: PAH concentration is recorded both as “Total PAH” and

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1367: 3302 1.6 mg/kg Total PAH

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: The PAHs in the soil sample are extracted into hexane:

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: acetone by shaking. The PAHs in the extract are separated UKAS

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: by gas chromatography and identified by the mass (All 16 PAH's)

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368:DETSC selective detector. The concentration of each PAH is MCERTS

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2020-0318-FFM-10035117-AUK-XX-XX-RP-ZZ-0117-01-Prairie_ESA_Addendum.pdf:1368: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:6:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:8: PAHS.

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: PAHs, phenol and TPH. Were taken from within the site boundary

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: sulphate cyanide and PAHs, phenol and TPH

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43:  Railway ballast containing metals and PAHs,

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: exception of PAH results.

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:47: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83:  PAHs – 1 sample (GAC 40mg/kg)

R-2020-0318-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:93: hydrocarbons, PAHs and BT

R-2020-0318-FFM-Phase II ESA.PDF:24: including tars, PAH, cyanides, thiocyanate, volatile

R-2020-0318-FFM-Phase II ESA.PDF:24: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2020-0318-FFM-Phase II ESA.PDF:24: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0318-FFM-Phase II ESA.PDF:24: Railways and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, and pH.

R-2020-0318-FFM-Phase II ESA.PDF:24: Above Ground Storage tanks (various) TPH, PAH, pH.

R-2020-0318-FFM-Phase II ESA.PDF:24: Metals, asbestos, TPH, PAH, VOC, SVOC,

R-2020-0318-FFM-Phase II ESA.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0318-FFM-Phase II ESA.PDF:25: Metals, TPH, PAHs, VOC, SVOC, cyanide, thiocyanate,

R-2020-0318-FFM-Phase II ESA.PDF:25: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0318-FFM-Phase II ESA.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0318-FFM-Phase II ESA.PDF:25: Water resources – Metals, ammoniacal nitrogen and PAH

R-2020-0318-FFM-Phase II ESA.PDF:26:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0318-FFM-Phase II ESA.PDF:29:Concentrations of PAH were measured in 90 of the 101 samples analysed. Statistical analysis indicates that,

R-2020-0318-FFM-Phase II ESA.PDF:29:within granular made ground, PAH concentrations were an order of magnitude higher than within slag dominant

R-2020-0318-FFM-Phase II ESA.PDF:29:Made Ground. Concentrations of PAH measured in cohesive Made Ground were a further order of magnitude

R-2020-0318-FFM-Phase II ESA.PDF:30:Leached concentrations of PAH were measured in all samples analysed and comprised a broad range of both

R-2020-0318-FFM-Phase II ESA.PDF:32:Where PAHs or TPH were detected they were generally measured only marginally above the MDL with the

R-2020-0318-FFM-Phase II ESA.PDF:40:The concentrations measured by third parties in excess of the GAC were all PAHs and are in line with the

R-2020-0318-FFM-Phase II ESA.PDF:42:of PCBs, PAHs and carbazole in soil via the vapour inhalation pathway – driven by vapour intrusion (pollutant

R-2020-0318-FFM-Phase II ESA.PDF:48:Concentrations of heavy metals, ammoniacal nitrogen, TPH, PAH and phenol were measured in excess of

R-2020-0318-FFM-Phase II ESA.PDF:52:Concentrations of manganese and PAHs have been measured in excess of WQS in more than half of the

R-2020-0318-FFM-Phase II ESA.PDF:52:of their MDL: magnesium, sulphate, sulphur, chloride, free cyanide, thiocyanate, selected PAHs, styrene,

R-2020-0318-FFM-Phase II ESA.PDF:53:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0318-FFM-Phase II ESA.PDF:53:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0318-FFM-Phase II ESA.PDF:53:screening the Made Ground and the superficial deposits. The highest concentrations of TPH, PAH and VOCs

R-2020-0318-FFM-Phase II ESA.PDF:56:including slag materials) and groundwater were assessed using GAC. Concentrations of arsenic and PAHs

R-2020-0318-FFM-Phase II ESA.PDF:56:Concentrations of arsenic, total cyanide and PAHs will need to be considered in the remedial strategy for the

R-2020-0318-FFM-Phase II ESA.PDF:72:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0318-FFM-Phase II ESA.PDF:73: PAH (ex. Naphthalene)

R-2020-0318-FFM-Phase II ESA.PDF:74:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2020-0318-FFM-Phase II ESA.PDF:494: Total PAH 14 2600 0.05 254 652

R-2020-0318-FFM-Phase II ESA.PDF:495: Total PAH 70 110000 0.05 1722 12974

R-2020-0318-FFM-Phase II ESA.PDF:496: Total PAH 5 14 0.49 4.26 4.97

R-2020-0318-FFM-Phase II ESA.PDF:497: USEPA 16 PAH 6 1700 0.05 214 562

R-2020-0318-FFM-Phase II ESA.PDF:509: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:509: PAH - USEPA 16, Total DETSC 3303 0.1 mg/kg 5.9 8.3 14

R-2020-0318-FFM-Phase II ESA.PDF:512: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:512: PAH - USEPA 16, Total DETSC 3303 0.1 mg/kg < 0.10 72 760

R-2020-0318-FFM-Phase II ESA.PDF:657: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:657: PAH Total DETSC 3304 0.2 ug/l 3.1 110 0.65

R-2020-0318-FFM-Phase II ESA.PDF:660: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:660: PAH Total DETSC 3304 0.2 ug/l 0.62 7800 11

R-2020-0318-FFM-Phase II ESA.PDF:663: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:663: PAH Total DETSC 3304 0.2 ug/l 4.3 4.1 1.1

R-2020-0318-FFM-Phase II ESA.PDF:680: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:680: PAH Total DETSC 3304 0.2 ug/l 2900 110 70

R-2020-0318-FFM-Phase II ESA.PDF:683: PAHs

R-2020-0318-FFM-Phase II ESA.PDF:683: PAH Total DETSC 3304 0.2 ug/l 13000 22 840

R-2020-0318-FFM-Phase II ESA.PDF:720: WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2020-0318-FFM-Phase II ESA.PDF:720: PAH MS (4 days), EPH (4 days)

R-2020-0318-FFM-Phase II ESA.PDF:720: 050 0.50 WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2020-0318-FFM-Phase II ESA.PDF:720: PAH MS (4 days), EPH (4 days)

R-2020-0318-FFM-Phase II ESA.PDF:721: 100 1.00 WATER (4 days), pH/Cond/TDS (1 days), Naphthalene, PAH MS, EPH

R-2020-0318-FFM-Phase II ESA.PDF:721: PAH MS (4 days), EPH (4 days)

R-2020-0318-FFM-Phase II ESA.PDF:725: days), Nitrite as N (2 days), PAH MS

R-2020-0318-FFM-Phase II ESA.PDF:726: days), Nitrite as N (2 days), PAH MS

R-2020-0318-FFM-Phase II ESA.PDF:726: days), Naphthalene (14 days), PAH

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:12:Only a limited number of samples were found to contain levels of arsenic, cyanide, or PAH above the

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:12:majority of the exceedances were for PAH and were in the area of the Cleveland Coke Ovens and

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:13: arsenic, cyanide, and selected PAH, originated from shallow soils across the site.

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:18:Concentrations of arsenic, cyanide and PAHs were measured in excess of the GAC in soil, driven by

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:18:free cyanide and PAHs will need to be considered in the remedial strategy for the site.

R-2020-0318-FFM-ROA and Remediation Strategy.PDF:31: from materials impacted with PAHs, asbestos, cyanide, and arsenic; and,

R-2023-0291-ESM-ES Vol 2 Green Lithium Appendix 14 - Contaminated Lands.pdf:38:1 - PAHs – Polycyclic Aromatic Hydrocarbons, TPH – Total Petroleum Hydrocarbons, VOC – Volatile Organic

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:13: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:15:cyanide, dibenzofuran, and PAHs that were measured in excess of the Generic Assessment Criteria

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 1).pdf:23: from materials impacted with lead, asbestos, dibenzofuran, and PAHs; and,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:5: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:5: tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:6: SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:17:benzene, dibenzofuran, 1,2 dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:19:metals, inorganics and PAH. This was not unexpected given that some of the sentinel wells were installed

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:23:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:23:(including tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:24:Contaminants associated with the above include metals, asbestos, hydrocarbons (including tars), PAH,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:24:potential to affect groundwater quality include metals, hydrocarbons, PAH, inorganics including cyanide,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:24:contaminants with the potential to affect groundwater quality include metals, TPH, PAH, VOC and SVOC.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:Similarly to metals, PAH and TPH are found throughout the site and are also likely 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:26:For PAH, the highest sum PAH concentration was measured in SBA_AUK_TP154 at 0.6m (99,000mg/kg),

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:coinciding with the highest sum TPH concentrations in the northeast of SBA. The next highest sum PAH

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:2,700mg/kg respectively). Similarly to TPH, further lower sum PAH concentrations were located across the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:26:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:27:Total PAH was measured above the laboratory MDL in all 52 monitored locations. Again, the highest

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:27:The sentinel wells which measured the highest total PAH concentrations were BH2010 (maximum 220µg/l)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:29:of metals and inorganics were measured above the MDL, along with a number of PAH compounds. Measured

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:33:  Hydrocarbons (including PAH, TPH and BTEX)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:40:site, exceed the SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:41:undertaken) for several of the wells where TPH or PAH concentrations exceed and may indicate entrainment

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:82: (representing one of the more mobile PAH), fluoranthene, anthracene and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:82:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:83: petroleum hydrocarbons, PAH and indicators included within the assessment are

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA - Detailed Quantitative Risk Assessment - South Bank.pdf:83:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:5: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:5: tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:6: SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:17:benzene, dibenzofuran, 1,2 dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:19:metals, inorganics and PAH. This was not unexpected given that some of the sentinel wells were installed

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:23:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:23:(including tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:24:Contaminants associated with the above include metals, asbestos, hydrocarbons (including tars), PAH,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:24:potential to affect groundwater quality include metals, hydrocarbons, PAH, inorganics including cyanide,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:24:contaminants with the potential to affect groundwater quality include metals, TPH, PAH, VOC and SVOC.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:Similarly to metals, PAH and TPH are found throughout the site and are also likely to be associated with the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:For PAH, the highest sum PAH concentration was measured in SBA_AUK_TP154 at 0.6m (99,000mg/kg),

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:coinciding with the highest sum TPH concentrations in the northeast of SBA. The next highest sum PAH

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:2,700mg/kg respectively). Similarly to TPH, further lower sum PAH concentrations were located across the

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:26:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:27:Total PAH was measured above the laboratory MDL in all 52 monitored locations. Again, the highest

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:27:The sentinel wells which measured the highest total PAH concentrations were BH2010 (maximum 220µg/l)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:29:of metals and inorganics were measured above the MDL, along with a number of PAH compounds. Measured

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:33:  Hydrocarbons (including PAH, TPH and BTEX)

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:40:site, exceed the SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:41:undertaken) for several of the wells where TPH or PAH concentrations exceed and may indicate entrainment

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:82: (representing one of the more mobile PAH), fluoranthene, anthracene and

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:82:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:83: petroleum hydrocarbons, PAH and indicators included within the assessment are

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0331-02-SB_DQRA.pdf:83:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 2).pdf:2:Metals (including heavy metals), PAHs,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 2).pdf:2:Metals (including heavy metals), PAHs, TPH,

R-2022-0096-CD-10035117-AUK-XX-XX-RP-ZZ-0408-02-Rem_Strat_South_Bank_West_Rev01 (Part 2).pdf:2:Metals, asbestos, TPH, PAH, cyanides,

R-2022-0096-CD-con land.pdf:2:dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2022-0096-CD-con land.pdf:2:identifying concentrations of lead, benzene, cyanide, dibenzofuran, NAPL and PAHs

R-2022-0096-CD-COMPLIANCE OFFICER REPORT.pdf:2:dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:2:Metals (including heavy metals), PAHs,

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:2:(including heavy metals), PAHs, volatile

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:2:Metals, TPH, PAH, VOC, SVOC, cyanides,

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:3:Metals (including heavy metals), PAHs,

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:3:(including heavy metals), PAHs, volatile

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 2.pdf:3:Metals, TPH, PAH, VOC, SVOC, cyanides,

R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 14.pdf:22:* Criteria of 0.00017 split between the sum of 5 PAH R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:69: PAH Glass 20g EPA Victoria 14 days - R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:70: PAH Glass 500 ISO 5667 3:2018 none 4 days R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: Soils and associated materials are extracted in dichloromethane (DCM) using sonication. The PAH concentration R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: is recorded both as “Total PAH” and as “Speciated PAH”, specified in terms of the 16 US EPA “Priority In-house method based on US EPA Method 8100, Polynuclear Aromatic R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: DETSC 3301 PAH in Soil by GC-FID UKAS (16 PAH's only) R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: 1.6 mg/kg Total PAH R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: Soils are extracted into hexane: acetone by shaking. The PAH concentration is recorded both as “Total PAH” and R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: as “Speciated PAH”, specified in terms of the 16 US EPA “Priority Pollutant” Polycyclic Aromatic In-house method based on US EPA Method 8100, Polynuclear Aromatic R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: DETSC 3302 Hexane / Acetone Extracted PAH in Soil by GC-FID Not Accredited R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: 1.6 mg/kg Total PAH R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: The PAHs in the soil sample are extracted into hexane: acetone by shaking. The PAHs in the extract are separated UKAS (All 16 PAH's) R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: by gas chromatography and identified by the mass selective detector. The concentration of each PAH is R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: (GC/MS) 0.10 mg/kg Total PAH R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: The PAHs in the water sample are extracted into dichloromethane by shaking. The PAHs in the extract are Semivolatile Organic Compounds by Gas Chromatography – Mass Spectrometry R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: separated by gas chromatography and identified by the mass selective detector. The concentration of each PAH is (GC/MS). R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 13.pdf:82: DETSC 3304 Polyaromatic Hydrocarbons in Waters by GC-MS 10 ng/l each UKAS (16 PAH's only) R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:13:contamination was characterised by elevated TPH. Concentrations of heavy metals and PAHs were typically R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:13: • Asbestos, metals, inorganic compounds and PAHs are present within the Made Ground, their wide- R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:16:potential sulphate attack in relation to buried concrete and contaminant attack (hydrocarbons, solvents, PAHs R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:23:select PAHs were measured in excess of WQS, these contaminants will be assessed further. R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:24:As shown in Appendix F several contaminants (including some metals, PAHs, and VOCs) do not have a readily R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:24:of their MDL: magnesium, thiocyanate, silicate, and selected PAHs. R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:25:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will be R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:25:made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective of R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:25:samples against appropriate WQS, various heavy metals, ammoniacal nitrogen and various PAHs were R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:25:metals, ammoniacal nitrogen, chloride, sulphate and selected PAHs. This section will discuss these R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:26:Exceedance of EQS (manganese, mercury, chloride, ammoniacal nitrogen, sulphate, selected PAHs) R-2022-0237-CD-10035117-AUK-XX-XX-RP-ZZ-0452-01-P4_GI_AD Part 1.pdf:26:Manganese, mercury, ammoniacal nitrogen, sulphate and select PAHs exceed the EQS within the well R-2021-0713-CD-Arcadis - South Bank Strategy.pdf:10: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons), R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:4: potential to affect groundwater quality include metals, hydrocarbons (including tars), PAH, R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:6: including TPH, metals, inorganics and PAH. This is not unexpected given that some of the R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:15:The GQRA concluded that concentrations of lead, benzene, dibenzofuran, and PAHs were measured R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:18:Contaminants associated with the above include metals, hydrocarbons (including tars), PAH, inorganics R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:19:(including tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:19:potential to affect groundwater quality include metals, hydrocarbons, PAH, inorganics including cyanide, R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:19:Similarly to metals, PAH and TPH are found throughout the site and are also likely to be associated with the R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:20:Total PAH was detected above the laboratory MDL in all monitored locations reported in Arcadis (2021), as 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:20:sentinel wells showed the highest total PAH concentrations measured in BH2010 and BH2025, with R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:21:of metals and inorganics were measured above the MDL, along with a number of PAH compounds. Measured R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:22: Speciated TPH PAH VOC Others R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:28:“For contaminants which are characterised by a high partition coefficient (e.g., some PAH compounds), the R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:29:Measured groundwater concentrations for a number of metals, cyanide, petroleum hydrocarbons, PAH R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:29:Ground source) exceeded EQS for a number of CoC including TPH, metals, inorganics and PAH. This is not R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61: * Criteria of 0.00017 split between the sum of 5 PAH

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0270-01-SBA_DQRA.pdf:61: 2 Indicator approach adopted for PAH inline with UK guidance. PAH with published

R-2021-0713-CD-COMPLIANCE OFFICER REPORT.pdf:2:concentrations of lead, benzene, dibenzofuran, and PAHs were measured exceeding

R-2021-0713-CD-Contam Land.pdf:1:concentrations of lead, benzene, dibenzofuran, and PAHs were measured exceeding

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:5: include metals, hydrocarbons including PAH, inorganics including cyanide, ammonia and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:5: tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:7: SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:17:benzene, dibenzofuran, 1,2 dichloroethane and PAHs were measured exceeding the Generic Assessment

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:19:metals, inorganics and PAH. This was not unexpected given that some of the sentinel wells were installed

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:23:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:23:(including tars), PAH, inorganics including cyanide, ammonia and sulphate and other volatile and semi-volatile

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:24:Contaminants associated with the above include metals, asbestos, hydrocarbons (including tars), PAH,

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:24:potential to affect groundwater quality include metals, hydrocarbons, PAH, inorganics including cyanide,

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:24:contaminants with the potential to affect groundwater quality include metals, TPH, PAH, VOC and SVOC.

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:25:Similarly to metals, PAH and TPH are found throughout the site and are also likely to be associated with the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:For PAH, the highest sum PAH concentration was measured in SBA_AUK_TP154 at 0.6m (99,000mg/kg),

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:coinciding with the highest sum TPH concentrations in the northeast of SBA. The next highest sum PAH

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:2,700mg/kg respectively). Similarly to TPH, further lower sum PAH concentrations were located across the

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:26:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:27:Total PAH was measured above the laboratory MDL in 35 of 39 monitored locations. Again, the highest

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:27:The sentinel wells which measured the highest total PAH concentrations were BH2010 (maximum 110µg/l)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:28:of metals and inorganics were measured above the MDL, along with a number of PAH compounds. Measured

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:33:  Hydrocarbons (including PAH, TPH and BTEX)

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:37:site, exceed the SSAC derived including hydrocarbons (TPH and PAH), phenols, cyanide, thiocyanate and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:38:undertaken) for several of the wells where TPH or PAH concentrations exceed and may indicate entrainment

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:67:Pyrene µg/L ~ 78 88 190 1.7 ~ Yes1 (representing one of the more mobile PAH), fluoranthene, anthracene and

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:67:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2021-0713-CD-10035117-AUK-XX-XX-RP-ZZ-0331-01-SB_DQRA.pdf:68:#6:Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:152:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:152:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:152:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:153:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:153:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:153:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:163:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:163:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:184:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:184:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:184: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:185: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:185: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf:535:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:241: trace metals, organotins, PAHs, PCBs, organochlorines, and PBDEs. No

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:241: observed for metals, PAHs, PCBs, and organochlorines. There are no formal

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:243:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:244:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:245:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:from DBT24. Exceedances for DIV for total PAH (40mg/kg) were also recorded in samples collected from

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:Soil analysis recorded TPH at a maximum concentration of 285mg/kg (at 2B3 at 3.0m bgl) and PAH at

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:271:Groundwater analysis recorded a maximum concentration of TPH at 62µg/l in 2B3 and total PAH at less

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:273: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:273: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, slag (heavy metals and metalloids, sulphates and sulphides), PAHs,

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274:plant) (60 m south east of the site boundary, Metals, PAHs, asbestos, sulphates and sulphides.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Fuel and oil hydrocarbons, metals and metalloids, PAHs, sulphates and sulphides.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Heavy metals, sulphates/ sulphides, PAHs, fuel and oil hydrocarbons and phenols.

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:274:Dockyards including saw and timber mills Metals and metalloids, sulphates and sulphides, PAHs, fuel and oil hydrocarbons,

MLA_2020_00507-PC1084-RHD-ZZ-XX-RP-Z-1100_EIA Report_Appendices_Part1-3.pdf:281:Benzole plant unsaturated Low Risk recorded exceedances for DIV for total PAH

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:152:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:153:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:163:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:163:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:184: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:185: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:185: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf:535:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:152:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:152:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:152:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:153:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:153:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:153:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:163:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:163:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:184:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:184:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:184: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:185: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:185: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf:535:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

R-2020-0684-ESM-Appendix 6_Sediment sampling plan.pdf:4: trace metals, organotins, PAHs, PCBs, organochlorines, and PBDEs. No

R-2020-0684-ESM-Appendix 6_Sediment sampling plan.pdf:4: observed for metals, PAHs, PCBs, and organochlorines. There are no formal

R-2020-0684-ESM-Appendix 6_Sediment sampling plan.pdf:6:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0684-ESM-Appendix 6_Sediment sampling plan.pdf:7:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0684-ESM-Appendix 6_Sediment sampling plan.pdf:8:Sample Station Metals Organotins THC PAHs PCBs PDBEs OCs PSA

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16:maximum concentration of 285mg/kg and PAHs at 25mg/kg. Groundwater analysis recorded a maximum

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16:concentration of TPH at 63µg/kg and PAHs at less than the laboratory detection limit.

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:16: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:17: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_8. Land quality and geology.pdf:17: • Travelling cranes and railways; Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:Virtually all samples recovered contained nearly all PAH compounds analysed for in concentrations above

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:Action Level 1 (and the TEL and PEL where available). There is no Action Level 2 for PAH compounds.

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:11:It should be noted that concentrations of PAH compounds within the Tees estuary have historically been

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:particularly heavy metals and PAH compounds. However, levels were not deemed high enough to prohibit

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:of individual PAH compounds were found in concentrations greater than three times Action Level 1.

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:12:formally quality assured for metals and PAHs, the parameters exceeding Cefas Action Level 1. This is for

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:22:The concentrations of PAHs and metals within the sediments in the Tees estuary could potentially affect

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_7. Marine sediment and water quality.pdf:22:is a highly precautionary approach given the preference of PAH compounds to remain adsorbed to

R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf:14:In terms of contaminants, the concentrations of PAHs and metals within the sediments in the Tees estuary

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:from DBT24. Exceedances for DIV for total PAH (40mg/kg) were also recorded in samples collected from

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:Soil analysis recorded TPH at a maximum concentration of 285mg/kg (at 2B3 at 3.0m bgl) and PAH at

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:25:Groundwater analysis recorded a maximum concentration of TPH at 62µg/l in 2B3 and total PAH at less

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:27: Fuel and oil hydrocarbons, metals and metalloid, PAHs, phenols, asbestos,

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:27: Phenols, PAHs, PCBs, bitumen, hydrochloric acid, organic compounds, fuel and oil

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, slag (heavy metals and metalloids, sulphates and sulphides), PAHs,

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28:plant) (60 m south east of the site boundary, Metals, PAHs, asbestos, sulphates and sulphides.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Fuel and oil hydrocarbons, metals and metalloids, PAHs, sulphates and sulphides.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Heavy metals, sulphates/ sulphides, PAHs, fuel and oil hydrocarbons and phenols.

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28: Asbestos, metals and metalloids, PAHs, fuel and oil hydrocarbons, volatile and semi-

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:28:Dockyards including saw and timber mills Metals and metalloids, sulphates and sulphides, PAHs, fuel and oil hydrocarbons,

R-2020-0684-ESM-PC1084-RHD-SB-EN-RP-EV-1107_Appendix 7_Land quality desk study.pdf:35:Benzole plant unsaturated Low Risk recorded exceedances for DIV for total PAH

R-2021-0405-FFM-10035117-AUK-XX-XX-RP-ZZ-0293-01-South Bank Quay Strategy rev1.PDF:20: from materials impacted with arsenic, asbestos and PAHs; and,

R-2021-0268-CD-10035117-AUK-XX-XX-CO-ZZ-0279-01-Railway_Bund_Memo.pdf:13:CE087 PAH (total of USEPA 16) Solvent extraction, GC-MS As received 0.34 mg/kg

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: GRO,BTEX, Phenols, PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: CH2M-SSI1 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: CH2M – SSI2 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: Within SSI Landholdings Sulphate, Chloride TPH, BTEX, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:23: Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:24:criteria adopted, with localised exceedances for PAH, lead and zinc.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:26: sulphate, TPH including tar, BTEX, phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:26: Asbestos, TPH and tars, BTEX, phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:27: Asbestos, hydrocarbons, ash, PAH, phenol, sulphates,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:27: Substations Asbestos, hydrocarbons, PAH, PCBs

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-04-Land West of Warrenby Redcar.pdf:27: Material Storage - Coal/coke breeze, ore, pellet, and PAH and metals

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:27: Phenols, PAH, VOC, SVOC,, nitrogen compounds

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

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: bitumen and PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:11: casting, tars, PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:13: macadam works and slag wool works immediately east, with Those above plus TPH, PAH and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: GRO,BTEX, Phenols, PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: CH2M-SSI1 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: CH2M – SSI2 Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: BTEX, Phenols, PAH, ammoniacal nitrogen

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Within SSI Landholdings Sulphate, Chloride TPH, BTEX, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Thiocyanate, Sulphate, TPH, Phenols, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:21: Sulphate, TPH, BTEX, Phenols, PAH, VOC,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:22:criteria adopted, with localised exceedances for PAH, lead and zinc.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Former industrial uses - iron and steel making plant Phenols, PAH, VOC, SVOC, PCB

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Asbestos, TPH, BTEX, Phenols, PAH, VOC, SVOC

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Railways Asbestos, hydrocarbons, ash, PAH, phenol, sulphates

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0520-01-Land West of Warrenby Redcar Preliminary Risk Assessment.pdf:24: Phenols, PAH, VOC, SVOC, PCB, ammoniacal nitrogen

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: for the Site, with the risks from asbestos and PAH mitigated by the requirement to import a

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:5: included metals, hydrocarbons including PAH and TPH, inorganics including cyanide,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:7: pathways in relation to asbestos (identified in shallow soils) and PAH (identified in

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:37:buildings or another suitable cover system. The depth at which the PAH exceedances were identified in

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:38:concentration of 1.2mg/kg. The SVOC 2-methylnaphthalene is a type of PAH, with detections of this compound

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:38:corresponding with samples in which the remaining PAH analysed were also measured. The remaining PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:39:A sample from S2-TPA83 at 3m bgl exceeded the GAC for two PAH compounds, which were considered to be

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:39:development. The depth at which PAH were measured in S1-BH13A is such that these pathways are not

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:46:Additional analysis has been undertaken to test for PAHs with a suitable MDL however the results of this are

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:46:of PAH (including eight compounds within the PAH suite and additionally carbazole, dibenzofuran, 2-

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:46:inorganics, TPH and PAH is required. It is noted that while certain metals are not considered to require further

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:detailed assessment. In addition, potentially active pollutant linkages have been identified in relation to PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:47:areas, which will act as a suitable cover system to break the linkages driving risk in relation to PAH and asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:48:selected metals and inorganics TPH and PAH is required.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:49:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:49:Contaminants associated with the above include metals, hydrocarbons (including tars), PAH, inorganics

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:50:well as potentially present as a result of anthropogenic sources. This includes metals, PAH (which could be

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:50:Associated contaminants with the potential to affect groundwater quality include metals, hydrocarbons, PAH,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:Similarly to metals, PAH and TPH are found throughout the Site. Generally, no discernible correlation with

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:albeit on the whole, the measured concentrations of TPH and PAH are likely to be associated with the imported

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:The highest concentrations of sum PAH in the hundreds of mg/kg were measured in S1-BH13A, located in the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:S2-TPA83, and as such, the PAH are likely to be associated with the presence of tar.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:51:As such, the presence of PAH and TPH in soil is considered to predominately be a diffuse source associated

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:analysed). The highest concentrations of sum PAH were associated with groundwater samples collected from

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:monitoring wells screening Made Ground (maximum concentration of sum PAH of 92µg/l), with maximum

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:measured concentrations of sum PAH concentrations in monitoring wells screening the superficial deposits and

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:Review of the lateral distribution indicates that concentrations of sum PAH were typically identified in the ones

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:surface material. Concentrations of sum PAH in the northern portion of the Site were typically less than 1µg/l.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:While it appears evident that elevated PAH in the south of the Site are likely associated with the historical land

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:manganese, TPH and PAH. Iron and manganese were identified in soils across the Site, albeit were

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:stocking area). TPH and PAH have also been measured in soils across the Site, again, likely due the Made

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:55:Ground. However, isolated elevated concentrations of TPH and PAH have also been identified, which may

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:56:• PAH, which were identified across the Site, albeit the highest concentrations were typically identified in the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:60:“For contaminants which are characterised by a high partition coefficient (e.g. some PAH compounds), the rates

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:63:analysis has been undertaken to test for PAHs with a lower MDL however the results of this are not available at

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:63:of this report on the basis that the risk from PAHs has been further evaluated below given that concentrations

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:63:of PAH in excess of the SSAC at 50m have been identified in the remaining data.

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:814: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:815: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:816: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:817: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:818: Sample Depth (m TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Nitrate Thiocyanate Asbestos

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:819: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:820: TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:821: Geology TPH PAH VOC SVOC PCB BTEX Phenols Sulphate Chloride Nitrate Thiocyanate

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:824: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:825: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:825: PAH FID

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:825: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:826: Naphthalene (14 days), Organic Matter (Manual) (730 days), PAH

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:829: PAH 16 Total mg/kg <16 <16 <22 <41 <16 <120 <50 <16 <16 <100 <16 <16 <17 <56 <16 <16

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:829: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:834: PAH 16 Total mg/kg <16 <22 <16 <309 <26 <18 <16 <16 <16 <16 <16 <16 <18 <16 <16 <16 <16 <16

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:834: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:839: PAH 16 Total mg/kg <16 <16 <18 <47 <16 <16 <16 <26 <16 <16 <16 <16 <16 <153 <16 <16 <16 <68

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:839: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:844: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:844: PAHs (Sum of total) mg/kg 0.43 <0.1 0.26 0.11 - <0.1 2.3 4.9 <0.1 - - 0.64 0.4 0.34 <0.1 1.3 <0.1 <0.1

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:849: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:849: PAHs (Sum of total) mg/kg <0.1 1.7 <0.1 0.75 <0.1 <0.1 <0.1 - <0.1 0.69 2.3 0.44 <0.1 <0.1 <0.1 0.3 1.8 <0.1

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:854: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:854: PAHs (Sum of total) mg/kg 1.5 <0.1 - <0.1 - <0.1 <0.1 74 1.3 <0.1 <0.1 - - - <0.1 <0.1 0.26 <0.1

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:859: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:859: PAHs (Sum of total) mg/kg 6.3 0.17 <0.1 <0.1 4 <0.1 3 - <0.1 <0.1 - <0.1 <0.1 <0.1 3.1 <0.1 <0.1 <0.1

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:864: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:864: PAHs (Sum of total) mg/kg - 7 - 0.22 0.16 <0.1 - 2.1 0.56 9.3 - 0.33 <0.1 - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:869: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:869: PAHs (Sum of total) mg/kg - - - - - <0.1 5.9 0.44 0.14 <0.1 <0.1 <0.1 0.81 <0.1 0.32 2.5 <14.91 2.9

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:874: PAH 16 Total mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:874: PAHs (Sum of total) mg/kg 0.44 0.44 <0.1 2.5 <0.1 <0.1 - 5.8 2.6 <0.1 - 7 0.4 - 31 <0.1 0.53 -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:879: PAH 16 Total mg/kg - - 0.15 4.4 4.3 0.37 25 2.3 0.31 4.2 2.2 1.1 3.4 9.8 0.12 1.6 0.71 0.05

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:879: PAHs (Sum of total) mg/kg 8.1 0.8 - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:884: PAH 16 Total mg/kg 3.6 0.35 1.1 0.67 - 1.8 - 0.63 - - 0.18 16 0.05 4.5 - 1.1 - 1.4

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:884: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:889: PAH 16 Total mg/kg 29 3.9 0.57 0.8 33 0.8 0.8 21 0.8 0.8 0.8 - 38 1.8 330 29 0.8 13

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:889: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:894: PAH 16 Total mg/kg 8.6 21 1.5 0.26 1.1 7.3 0.74 14 0.05 - - 34 1.1 - 30 6 0.05 8.2

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:894: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:899: PAH 16 Total mg/kg 3.2 1.6 0.57 0.61 - 38 1.8 5 0.05 9.6 4.1 - 0.34 0.05 2.4 0.53 3.2 -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:899: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:904: PAH 16 Total mg/kg 0.05 - 0.05 0.67 - - 7.7 1.5 - - - - 1.6 - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:904: PAHs (Sum of total) mg/kg - - - - 1.3 <0.1 - - - 5.8 - 1.6 - - 1.9 0.91 97 -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:909: PAH 16 Total mg/kg - - 0.99 10 7.7 1.2 0.75 0.05 - 0.49 0.16 15.94 0.05 1.8 0.05 2.7 2.5 2.1

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:909: PAHs (Sum of total) mg/kg 3.9 - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:914: PAH 16 Total mg/kg 0.05 1.1 0.05 - 0.55 0.56 0.05 0.05 1.1 4.1 - 0.2 11 0.05 1.1 0.05 10 1.4

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:914: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:919: PAH 16 Total mg/kg 6.4 0.05 38 150 44 0.21 0.15 38 670 43 27 - 0.05 1.8 0.05 6.8 0.21 0.05

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:919: PAHs (Sum of total) mg/kg - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:924: PAH 16 Total mg/kg 1.7 1.2 0.05 -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:924: PAHs (Sum of total) mg/kg - - - 0.49

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:936: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:937: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:938: PAHs (Sum of total) µg/L - - - - - - - - - - 15 - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:939: PAHs (Sum of total) µg/L - - - - - - - - - - - - - - - - - - <0.2

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:941: PAH 16 Total µg/L <160 <160 <160 - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:941: PAHs (Sum of total) µg/L - - - 0.61 <0.2 - <0.2 0.63 0.28 - - 0.39 <0.2 - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:946: PAH 16 Total µg/L - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:946: PAHs (Sum of total) µg/L 0.38 0.36 - - 0.52 - - 0.23 - - - 0.22 0.5 -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:951: PAH 16 Total µg/L - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:951: PAHs (Sum of total) µg/L 0.21 0.76 - - - - 0.39 0.2 - - - - 6.8 - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:956: PAH 16 Total µg/L - - - - - - - - - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:956: PAHs (Sum of total) µg/L 5.6 1.5 - - 0.42 - - 2.9 9.6 5.3 0.22 0.4 2.4 19 62 92 1.1 7.6 14 3.5

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:961: PAH 16 Total µg/L - - - - - - - - - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:961: PAHs (Sum of total) µg/L 0.13 0.25 3 0.05 0.08 0.94 <0.2 0.26 - - - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:967: Volatile Organic Compounds, asbestos and Polychlorinated Biphenyls data was analysed from 2017 onwards. It is noted that while the 2004 Enviros investigation included speciated PAH analysis, only the sum PAH analytical testing data from this

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:967: investigation is presented here (51No. samples analysed for speciated PAH). This is due to the nature of the data provided for review; as such, while the measured concentrations have been included in the consideration of the human health risk assessment

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:967: for the individual PAH fractions, they have not been included in this screening table.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:969:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:970:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:972:6 The compounds detected are PAH, with a review of the distribution of the remaining PAH for which criteria were available for comparison indicating that they were typically identified in the same location and at similar concentrations. As such, the remaining PAH for which WQS are available for comparison have been

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:972:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the corresponding AA-EQS in water.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:972: Yes(ii) Compounds associated with Polycylic Aromatic Hydrocarbons have been assessed further via and an indicator compound approach. Indicator compounds have been selected based on readily available MRV, WQS for either EQS, DWS or both and following a review of PAH concentrations to ensure they represent the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:972: PAH present. Concentrations of all 16 PAH compounds were measured above the MDL in the leachate and Made Ground. The indicator compounds selected represented a relatively high proportion of the contaminant mass identified. Within the superficial and bedrock, measured PAH concentrations were generally

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:972: lower with some PAH below the MDL. However, at least some of the PAH indicators selected were measured above WQS and/or MDL. As such, The use of indicator compounds for assessment of PAH is considered appropriate to represent the risk from the 16 PAH.

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:975:#10:Water Supply (Water Quality) Regulations 2016. Value of 0.1µg/l for PAH split between four individual PAH. Requires

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:977: PAHs (Sum of total) µg/L 2 1 15 - -

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:977:See BaP Water Framework Directive (Standards and Classification) Directions (England and Wales) 2015. Benzo(a)pyrene can be considered as a marker for other PAH for comparison with the

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0428-04-LWoW_DQRA.pdf:983: contamination was identified (samples containing sum PAH greater than 1mg/kg were excluded). The SOM was converted

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:18:Levels of PAH were measured above the screening criteria in three locations, the SPL linkage for these

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:25: from materials impacted with asbestos, and PAHs; and,

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:25: Ground. This approach is also considered suitable to treat the PAH measured above the screening

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:33:Where contaminants other than asbestos or NAPL (such as PAH and the pollutant linkages identified

R-2022-0755-CD-10035117-AUK-XX-XX-RP-ZZ-0417-06-Rem_Strat_LWoW(1).pdf:49:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:12:Only a limited number of samples were found to contain levels of arsenic, cyanide, or PAH above the

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:12:majority of the exceedances were for PAH and were in the area of the Cleveland Coke Ovens and

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:13: arsenic, cyanide, and selected PAH, originated from shallow soils across the site.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:18:Concentrations of arsenic, cyanide and PAHs were measured in excess of the GAC in soil, driven by

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:18:free cyanide and PAHs will need to be considered in the remedial strategy for the site.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0066-01-Prairie ROA and Strategy.PDF:31: from materials impacted with PAHs, asbestos, cyanide, and arsenic; and,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: PAH is extracted from one litre of filtered water sample by

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:94: Note for PAH by SPE

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: dichloromethane (DCM) using sonication. The PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: concentration is recorded both as “Total PAH” and as

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: PAH concentration is recorded both as “Total PAH” and

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:113: 3302 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: The PAHs in the soil sample are extracted into hexane:

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part6.PDF:114: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:6: A range of metals, phenols, aliphatic hydrocarbons, PAHs VOCs, SVOCs and aromatic hydrocarbon

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:8: PAHS.

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:25: Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:25: PAHs, phenol and TPH. Were taken from within the site boundary

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:25: sulphate cyanide and PAHs, phenol and TPH

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:26: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:26: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:43: Railway ballast containing metals and PAHs,

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:43: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:44: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:44: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:45: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:45: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:46: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:46: exception of PAH results.

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:46: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:46: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:47: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:83: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:83: PAHs 1 sample (GAC 40mg/kg)

R-2021-0879-FF-41825-WOOD-XX-XX-RP-OC-0001_S0-P01 (Part 1).pdf:93: hydrocarbons, PAHs and BTEX compounds

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: including tars, PAH, cyanides, thiocyanate, volatile

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, cyanides, thiocyanate,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Railways and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, and pH.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Above Ground Storage tanks (various) TPH, PAH, pH.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:24: Metals, asbestos, TPH, PAH, VOC, SVOC,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, TPH, PAHs, VOC, SVOC, cyanide, thiocyanate,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:25: Water resources – Metals, ammoniacal nitrogen and PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:26:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:Concentrations of PAH were measured in 90 of the 101 samples analysed. Statistical analysis indicates that,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:within granular made ground, PAH concentrations were an order of magnitude higher than within slag dominant

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:29:Made Ground. Concentrations of PAH measured in cohesive Made Ground were a further order of magnitude

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:30:Leached concentrations of PAH were measured in all samples analysed and comprised a broad range of both

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:32:Where PAHs or TPH were detected they were generally measured only marginally above the MDL with the

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:40:The concentrations measured by third parties in excess of the GAC were all PAHs and are in line with the

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:42:of PCBs, PAHs and carbazole in soil via the vapour inhalation pathway – driven by vapour intrusion (pollutant

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:48:Concentrations of heavy metals, ammoniacal nitrogen, TPH, PAH and phenol were measured in excess of

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:Concentrations of manganese and PAHs have been measured in excess of WQS in more than half of the

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:of their MDL: magnesium, sulphate, sulphur, chloride, free cyanide, thiocyanate, selected PAHs, styrene,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:52:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:53:screening the Made Ground and the superficial deposits. The highest concentrations of TPH, PAH and VOCs

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:56:including slag materials) and groundwater were assessed using GAC. Concentrations of arsenic and PAHs

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part1.PDF:56:Concentrations of arsenic, total cyanide and PAHs will need to be considered in the remedial strategy for the

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:2:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:3: PAH (ex. Naphthalene)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part2.PDF:4:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: PAH is extracted from one litre of filtered water sample by

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:111: Note for PAH by SPE

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: dichloromethane (DCM) using sonication. The PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: concentration is recorded both as “Total PAH” and as

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: PAH concentration is recorded both as “Total PAH” and

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:130: 3302 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: The PAHs in the soil sample are extracted into hexane:

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part5.PDF:131: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:12:Concentrations of PAH were measured in 4 of the 5 samples analysed and concentrations of TPH were

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:13:Low levels of PAH were measured in the majority of samples with higher concentrations recorded in

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:22:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0117-02-Prairie_ESA_Addendum_Part1.PDF:22:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: PAH is extracted from one litre of filtered water sample by

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: Low Level PAH solid phase extraction. PAH is eluted from the SPE column

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:23: Note for PAH by SPE

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: dichloromethane (DCM) using sonication. The PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: concentration is recorded both as “Total PAH” and as

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42:DETSC PAH in Soil by “Speciated PAH”, specified in terms of the 16 US EPA UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: 3301 GC-FID “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. (16 PAH's only)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Hydrocarbons 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: PAH concentration is recorded both as “Total PAH” and

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Hexane / Acetone as “Speciated PAH”, specified in terms of the 16 US EPA In-house method based on US EPA

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: Extracted PAH in “Priority Pollutant” Polycyclic Aromatic Hydrocarbons. Method 8100, Polynuclear Aromatic Not Accredited

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:42: 3302 1.6 mg/kg Total PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: The PAHs in the soil sample are extracted into hexane:

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: acetone by shaking. The PAHs in the extract are separated UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: by gas chromatography and identified by the mass (All 16 PAH's)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43:DETSC selective detector. The concentration of each PAH is MCERTS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: Soils by GC-MS Compounds by Gas Chromatography – PAH

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: The PAHs in the water sample are extracted into Method 8270- US EPA Method 8270,

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: dichloromethane by shaking. The PAHs in the extract are Revision 3, Semivolatile Organic

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43:DETSC mass selective detector. The concentration of each PAH is Mass Spectrometry (GC/MS) UKAS

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:43: 3304 determined by referencing individual mass peak areas to (16 PAH's only)

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:55: Total PAH 14 2600 0.05 254 652

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:56: Total PAH 70 110000 0.05 1722 12974

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:57: Total PAH 5 14 0.49 4.26 4.97

R-2021-0879-FF-10035117-AUK-XX-XX-RP-ZZ-0062-02-Prairie_ESA_Part6.PDF:58: USEPA 16 PAH 6 1700 0.05 214 562

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:2: PAHs (as BaP equivalent) 0.003

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:2: Emission concentration for PAHs taken from Figure 8.119 of the Best Available Techniques (BAT) Reference Document on

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:3: PAHs 0.003 (d)

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:4: and PAHs. Member states must comply with the limit values (which are legally binding on the

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:5: PAHs (as BaP equivalent) Annual (a) 0.00025 μg.m-3

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:6: PAHs (as BaP equivalent) 0.00025 -

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:13: results are provided in Appendix 11.7. For the pollutants not in the IED, NH3, PAHs and PCBs

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:13: PAHs – BaP - 1.66E-04 1.66E-04

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:19: PAHs 0.21 ng.m-3 - Monitored (PAH Network)

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:27: PAHs 1 hour (annual mean) 0.00025 6.43E-05 26 1 Yes

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:27: NO2, Cd (cadmium), As (arsenic), Co (cobalt), Pb (lead), Mn (manganese), Ni (nickel) and PAHs.

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:27: PAHs 1 hour (annual mean) 0.00025 0.00021 0.00028 110 Yes

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:28: 11.6.15 For PAHs, the PEC is 100% of the EAL, therefore the long-term PAH impact based on modelling

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:28: than 1% of the EAL and the long-term PAH impacts are considered to be insignificant.

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:30:11.7.5 For PAHs, Table 11.23shows that the maximum non-cumulative PEC across the modelled grid is

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:30: only developments identified that could have a cumulative effect with regards to PAHs. The annual

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:30: mean PAH impact of the Graythorp Energy Centre is less than 0.5% of the AQAL, therefore the

R-2020-0411-FFM-Chapter 11 Air Quality.pdf:31: 1.1 km from receptor 3. On this basis, the cumulative effect of PAHs is not considered to be

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:2:Table 1.10: Annual-mean PAHs Concentrations (ng.m-3) ……………………………………………………………………….4

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6:1.1.21 The polycyclic aromatic hydrocarbon (PAH) network monitors ambient concentrations of PAHs at

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6: 31 sites in the UK. At the majority of sites, only solid PAHs are monitored; both gaseous and solid

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6: PAHs are only monitored at two locations.

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6:1.1.22 The nearest site monitoring solid PAHs is Middlesbrough. The nearest site monitoring both

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6: gaseous and solid PAHs is Auchencorth Moss, however the site has been closed since 2014.

R-2020-0411-FFM-Appendix 11.2 - Detailed Baseline Assessment.pdf:6:Table 1.10: Annual-mean PAHs Concentrations (ng.m-3)

R-2020-0411-FFM-11366_REC Planning Statement_S_AS.pdf:85: (cadmium), As (arsenic), Co (cobalt), Pb (lead), Mn (manganese), Ni (nickel) and PAHs. Further, it

R-2020-0411-FFM-11366_REC Planning Statement_S_AS.pdf:85:6.6.12 For PAHs, the PEC is 100% of the EAL, therefore the long-term PAH impact, based on modelling

R-2020-0411-FFM-11366_REC Planning Statement_S_AS.pdf:86: the long-term PAH impacts are considered to be insignificant.

R-2020-0411-FFM-Appendix 11.7 - WI BAT Results.pdf:4: (arsenic), Co (cobalt), Pb (lead), Mn (manganese), Ni (nickel) and PAHs.

R-2020-0411-FFM-Appendix 11.7 - WI BAT Results.pdf:5:1.1.8 For PAHs, the PEC is 110% of the EAL, therefore the long-term PAH impact based on modelling

R-2020-0411-FFM-Appendix 11.7 - WI BAT Results.pdf:5: predicted PC is less than 1% of the EAL and the long-term PAH impacts are considered to be

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:13: lead, benzene, naphthalene, dibenzofuran and PAHs (polycyclic aromatic hydrocarbons),

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:15:benzene, dibenzofuran, and PAHs that were measured in excess of the Generic Assessment Criteria

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:22: from materials impacted with Lead, arsenic, asbestos, cyanide, and PAHs; and,

R-2021-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0271-02-South Bank Priority Strategy.pdf:41:Metals, asbestos, TPH including tars, PAH, cyanides,

R-2023-0179-SCP-HyGreen Production Facility Scoping Report_FINAL.pdf:4: PAH Polycyclic Aromatic Hydrocarbon

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:23: Steelworks. compounds (VOCs and SVOCs), PAHs, PCBs and phenols.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:23: cyanides, petroleum hydrocarbons, PAHs, PCBs, phenols,

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:23: adjacent to railway. phenols and PAHs.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:23: ammonia and PAHs.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:24: PAHs.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:24: and PAHs.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:24: Geotechnics Ltd 2020 sulphur species, petroleum hydrocarbons, PAHs, PCBs and

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:24: Reports chloride, sulphate, petroleum, hydrocarbons, PAHs and

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:24: sulphur, petroleum hydrocarbons, PAHs and phenols.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:31: Conceptual Site Model Review and Risk Assessment A rcadis 2020 H1. Concentrations of PAH

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:32:H4.62 Statistical analysis indicates that, within granular Made Ground, PAH concentrations were an

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:32: order of magnitude higher than within slag dominant Made Ground. Concentrations of PAH

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:32:H4.63 Leached concentrations of PAH were measured in all sam ples analysed and comprised a broad

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:32: were generally lower than those observed in Made Ground. Where PAHs or TPH were detected

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:33: screening criteria for copper and manganese, and several PAH compounds. Contaminant

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:34: including heavy metals, PAH, hydrocarbons, abnormal pH and sulphate/sulphides. The

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:34: human health receptors were arsenic, and PAHs including naphthalene. Contaminants in

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:35: 2 Dermal contact/ingestion of soil from arsenic, and PAHs including naphthalene associated

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:36: breaks from materials impacted with PAHs, asbestos, cyanide, and arsenic; and,

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:37: were arsenic, and PAHs including naphthalene.

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:42: PAHs) determinands and there is therefore a requiremen t for its collection and treatment prior

R-2020-0819-ESM-VOL 2 CHAPTER H.pdf:46: 17 PAH Polycyclic Aromatic Hydrocarbons

R-2020-0819-ESM-Dorman Point - Planning Statement - Dec 2020.pdf:52: range of contaminants including heavy metals, PAH, asbestos, hydrocarbons, abnormal pH and

R-2020-0819-ESM-Dorman Point - Planning Statement - Dec 2020.pdf:52: materials impacted with PAHs, asbestos, cyanide, and arsenic; and, reduce the geotechnical

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:4: included metals, hydrocarbons including PAH and TPH, inorganics including cyanide,

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:25:system. The depth at which the lead and PAH exceedances were identified are such that direct contact

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:25:concentration of 1.2mg/kg. The SVOC 2-methylnaphthalene is a type of PAH, with detections of this compound

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:25:corresponding with samples in which the remaining PAH analysed were also measured. The remaining PAH

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:30:hydrocarbons including PAH, inorganics including cyanide, ammonia and sulphate, asbestos and limited

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:31:Contaminants associated with the above include asbestos, metals, hydrocarbons, PAH, inorganics including

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:31:well as potentially present as a result of anthropogenic sources. This includes metals, PAH (which could be

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:31:Associated contaminants with the potential to affect groundwater quality include metals, hydrocarbons, PAH,

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:The levels of PAH and TPH are generally of similar magnitude across the three DGA, however only

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:In soil, maximum sum PAH and TPH concentrations were measured at 1.00m bgl in F-BH102 within the former

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:Redcar works area. Sum PAH and TPH across the rest of the DGA is one to two orders of magnitude lower

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:Made Ground elsewhere. A similar distribution is noted for PAH in soil leachate, sum TPH was only measured

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:(Arcadis 2022b), namely the presence of PAH and TPH in soil is considered to predominately be a diffuse

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:32:selenium), PAH, TPH, and inorganic ions (including ammoniacal nitrogen, cyanide, sulphate, and thiocyanate).

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:441: PAHs

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:448: PAHs by GC-MS.

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:455: PAHs

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:465: PAHs by GC-MS.

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:473: PAHs

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:482: PAHs by GC-MS.

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:490: PAHs

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:500: PAHs by GC-MS.

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:508: PAHs

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:518: PAHs by GC-MS.

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:528:PAH PAH 16 Total mg/kg 5.6 3.4 <0.1 <0.1 <0.1 <0.1 <0.1 2.4 <0.1 <0.1 0.22 <0.1

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:532:PAH PAH 16 Total <0.1 5.8 - 4.7 9.4 8.3 3.2 3 3.2 10 15 0.32

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:536:PAH PAH 16 Total 0.74 <0.1 - <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 0.13

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:540:PAH PAH 16 Total <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 0.3 - 0.93

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:544:PAH PAH 16 Total <0.1 0.39 - 21 20 <0.1 - <0.1 2.9 0.77 0.64 0.5

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:548:PAH PAH 16 Total <0.1 <0.1 - - - 98 18 - 0.62 0.24 - <0.1

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:552:PAH PAH 16 Total <0.1 2.7 8.5 350 - 0.39 <0.1 <0.1 0.51 1 - <0.1

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:556:PAH PAH 16 Total <0.1 <0.1 - - -

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:561:PAH PAH (total, NSW Waste 2008) µg/L 0.39 0.34 <0.2 0.28 <0.2 - 1.1 0.71 0.29 - - 0.35 0.24 0.28 <0.2 0.26 <0.2 -

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:562:PAH PAH (total, NSW Waste 2008) 0.21 <0.2 <0.2 <0.2 <0.2 1.3 <0.2 - - - 0.3 <0.2 - - 5.7 <0.2 - -

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:565: PAH Naphthalene 2 µg/L <0.1 <0.1 <0.1 <0.1 <0.1 0.026 0.051

R-2023-0277-CD-10035117-AUK-XX-XX-RP-ZZ-623-01-Data Gap Areas GQRA.pdf:565: PAH 16 Total µg/L 1.125 <0.173 <0.173 <0.173 0.238 0.032 0.659

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:20: analysed for asbestos, heavy metals, PAH,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:20: metals, PAH, cyanides, pH, sulphate, phenols, and

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:20: Investigation HFO analysed for PAH, petroleum hydrocarbons and

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:21: Phase II Environmental metals, PAH, cyanides, thiocyanate, pH, sulphate,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:21: heavy metals, PAH, cyanides, thiocyanate, pH,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:21: metals, PAH, cyanides, thiocyanate, pH, sulphate,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:21: heavy metals, PAH, cyanides, thiocyanate, pH,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:21: conducted September – metals, PAH, cyanides, thiocyanate, pH, sulphate,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:22: heavy metals, PAH, cyanides, thiocyanate, pH,

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:27: excavated. Elevated concentrations of PAH (Polycyclic Aromatic Hydrocarbns) and petroleum

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:32: concentrations of metals, TPH and PAH compounds were recorded above the Water Quality

R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter H - Ground Conditions - Dec 2020.PDF:40: 12 PAH Polycyclic Aromatic Hydrocarbons

R-2020-0465-FFM-Officer report _R20200465FFM.pdf:5:Standards for metals and PAH. An assessment of groundwater and surface

R-2020-0465-FFM-Officer report _R20200465FFM.pdf:10:Standards for metals and PAH. An assessment of groundwater and surface

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:6:  A range of metals, phenols, aliphatic hydrocarbons, PAH’s VOCs, SVOCs and aromatic hydrocarbon

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:8: PAHS.

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25:  Analysis of 60 samples for Heavy metals, Pahe, Phenols and Toluene extractable

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: PAHs, phenol and TPH. Were taken from within the site boundary

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:25: sulphate cyanide and PAHs, phenol and TPH

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: TPH and PAHs in all nine samples were low with TPH at a maximum of 100mg/kg and

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:26: 1B1 in January 2007. PAHs and BTEX were all below detection. No groundwater level data was

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43:  Railway ballast containing metals and PAHs,

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:43: In 2008, Enviros investigations encountered elevated PAHs and Extractable hydrocarbons in Made

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: sulphate, sulphur, cyanide, phenols, PAHs and TPH. No interpretation of the data was undertaken

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:44: phenols, PAHs and TPH. (CH2M compared the results to GACs, as summarised above.) Two

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: phenols, sulphates, sulphur, PAHs and TPH. The contaminants were generally below the GAC

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:45: use. TPH, PAH species and phenol results were all less than the GACs for commercial/ industrial

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: products plant. PAHs exceeded the GAC in the area of the Coke Oven and By-products plant.

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: exception of PAH results.

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: GAC. Selected determinands including vanadium, zinc, cyanide, toluene, PAHs, hydrocarbons and

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:46: groundwater), with respect to elevated PAHs and hydrocarbons at the former Coke Works and By-

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:47: hydrocarbons, PAHs and BTEX compounds were elevated above screening criteria at the former

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83: The site held a COMAH upper tier establishment classification associated with PAH in the Coke

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:83:  PAHs – 1 sample (GAC 40mg/kg)

R-2020-0465-FFM-41825-WOOD-XX-XX-RP-OC-0001_S0_P01.PDF:93: hydrocarbons, PAHs and BT

R-2020-0465-FFM-R 20 0465 Con Land.pdf:1:for metals and PAH. An assessment of groundwater and surface water quality has

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:13: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:13: Railway lines and sidings Metals, asbestos, TPH, PAH, VOC, SVOC, PCB, and pH.

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:14: Metals (including heavy metals), PAH, cyanide,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:14: Metals, asbestos, TPH, PAH, acids and bases, VOCs,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:14:material composition (e.g. metals, inorganics, asbestos and PAHs) will be assessed separately for each

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:15:Concentrations of PAH were measured in 29 of the 32 soil samples analysed, and in all eight samples of soil

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:24:An exceedance of the EQS for five metals were recorded. Five PAH were measured in excess of DWS with

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:25:Given a number of PAHs do not have readily available WQS, assessment of the risk to water resources will

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:25:be made using PAHs in groundwater that have available WQS. This is considered to be sufficiently protective

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:25:Concentrations of PAH have been measured in excess of WQS in the majority of leachate samples. Of the

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:25:measured concentrations of PAH in excess in leachate, the majority are considered to be marginally in excess

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:25:of the WQS. Given this, and that PAH are generally of low mobility in the natural environment, the risk to water

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:33:Metals (including heavy metals), PAHs, VOC,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:33:Metals (including heavy metals), PAHs,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:33:Metals, asbestos, TPH, PAH, cyanides,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:34:Metals (including heavy metals), PAHs,

R-2020-0465-FFM-10035117-AUK-XX-XX-RP-ZZ-0125-01-MPA_Shallow_Soils.PDF:34:Metals, asbestos, TPH, PAH, cyanides,

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:7: PAHs 0.00025 Annual - AQS Objective

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:12: the Middlesbrough AURN site. For the assessment of baseline concentrations of PAHs, only

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:12: monitored concentrations of benzo-a-pyrene (BaP) have been considered as this is the only PAH

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:18: PaHs 0.18 ng/m³ Maximum background concentration

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:37: PAHs Annual mean pg/m³ 250 180 4.23 3.85 3.64 3.69 3.42 4.23 1.69% 184.23 73.69%

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:39: • Annual mean PAHs;

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: 7.2.5 Annual mean PAHs

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: The annual mean PAHs (as BaP) PC from the Proposed ERF is predicted to be 1.67% of the AQAL at

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: Table 35 shows the annual mean PAH PC at the identified sensitive human receptor locations. PCs

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:43: Table 35: Annual Mean PAHs (as BaP) Impact at Identified Sensitive Receptors

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:81: Annual Mean PAHs (as

R-2023-0227-CD-TV_ERF_Air_Quality_Emissions_Modelling_Report.pdf:81: Figure 13 - Annual Mean PAHs