BC CSR Omnibus Amendment: A Case Study on the Impacts to Environmental Investigation and Remediation
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1 BC CSR Omnibus Amendment: A Case Study on the Impacts to Environmental Investigation and Remediation By: Karey Dow, P.Ag., PMP, Senior Project Manager, Hemmera May 2017
2 Agenda What is Omnibus Key Updates Case Study on Typical Sites Petroleum Hydrocarbons Solvents (TCE) Metals Key Takeaways 000
3 What is Omnibus a volume of reprinted works of a single author or of works related in interest or theme. pertaining to, including, or dealing with numerous objects or items at once
4 Key Omnibus Updates CSR Stage 10 Amendments coming November 1, 2017: Update and add standards to current science Eliminate Schedule 7 Soil Relocation standards Add new Parkade vapour standards Establish new Low & High Density Residential land use standards Add 2 new Wildland standards natural & reverted New/Updated supporting Guidance and Protocols
5 Case Studies on Typical Sites
6 Case Study #1: Hydrocarbons in Soil Impact of Omnibus: Benzene, ethylbenzene, and xylenes essentially the same SV/MW13 1 BH13 04 BH7 Toluene becomes a COC M13 06 Overall: Minimal Impact BH SV/MW13 8 SV/MW13 7 BH6 Toluene>2.5 ppm (Current) Toluene>0.3 ppm (Omnibus) SV/MW M13 03 SV/MW M13 05 BH1 BH2 SV/MW13 2 BH13 07 Ethylbenzene >7 ppm & BH13 02 Xylenes>20 ppm (Current) BH4 UST Nest MW15 302S/D SV/MW13 10 BH5 12 BH102 MW15 301S/D SV/MW13 9 BH13 01 BH13 01 SV/MW13 4 SV/MW BH3 12 BH101 SV/MW13 3 BH13 02 Benzene>0.03 ppm (Omnibus) Benzene>0.04 ppm (Current) SV/MW13 5 Ethylbenzene>10 SV/MW13 6 ppm & SV/MW Xylenes>4.5 ppm (Omnibus)
7 Case Study #1: Hydrocarbons in Groundwater Impact of Omnibus: Benzene (driver for newer releases): MW no change for DW AW MW Toluene: DW AW Ethylbenzene (driver for older releases: DW No change for AW Xylenes: DW AW Overall: Minimal Impact SV/MW SV/MW BH SV/MW M13 03 MW SV/MW MW SV/MW13 8 Ethylbenzene >2.4 ppb (Current) Ethylbenzene >140 ppb (Omnibus) Benzene >5 ppb (Current) Benzene >5 ppb (Omnibus) M13 05 M13 06 BH1 SV/MW SV/MW13 7 BH2 SV/MW13 10 SV/MW13 9 BH3 SV/MW13 1 BH13 04 BH7 BH13 02 BH BH101 BH5 BH4 SV/MW13 4 SV/MW13 3 BH13 02 BH6 SV/MW13 2 BH13 07 UST Nest 12 BH102 BH13 01 SV/MW13 5 SV/MW SV/MW13 6
8 Case Study #2: TCE in Soil Impact of Omnibus: Additional delineation TCE>0.65 ppm (Current) Off site contamination Introduces a third party Additional CoC Increased volume of soil disposal BH3(B) BH115(A) BH115(B) BH21(A) BH6(C) BH4(C) BH12(A) MW BH11(A) BH17(A) BH20(A) BH19(A) BH18(A) BH5(C) BH13 BH14(A) BH23(A) BH22(A) VW BH3(A) MW BH2(B) BH16(A) BH15(A) BH4(B) BH2(C) BH1(B) BH5(D) MW BH10(B) BH4(D) BH8(C) MW BH1(D) BH2(D) BH7(C) BH11(B) BH20(B) BH14(B) BH3(C) MW BH6(D) BH12(B) BH9(B) BH15(B) BH19(B) BH18(B) BH17(B) BH16(B) BH30 BH25 BH23(B) BH21(B) BH22(B) BH24 BH26 BH1(C) MW07 04 MW17 02 MW07 01 MW17 03 MW TCE>0.3 ppm (Omnibus) MW MW BH7(B) MW EMW 1 BH8(B) MW EMW 2 = ~ extra $50K MW MW MW MW MW TCE>0.015 ppm (Current DW) MW MW BH35 BH10(A) BH32 BH33 BH34 BH9(A) BH31 MW BH02M BH06M BH01M
9 Case Study #2: TCE in Vapour Impact of Omnibus: Less delineation Impacts remain on site Removes high risk condition No contamination if building a parkade TCE>0.5 µg/m 3 (Current) Could get a CoC prior to construction BH3(B) BH115(A) BH115(B) MW BH21(A) BH6(C) BH4(C) BH12(A) MW BH11(A) BH17(A) BH20(A) BH19(A) BH18(A) BH5(C) BH13 MW BH14(A) BH23(A) BH22(A) VW BH3(A) MW BH2(B) BH16(A) BH15(A) BH4(B) BH2(C) BH1(B) BH5(D) MW BH10(B) BH4(D) BH8(C) MW BH1(D) BH2(D) BH7(C) BH11(B) BH20(B) BH14(B) BH3(C) MW BH6(D) BH12(B) BH9(B) BH15(B) BH19(B) BH18(B) BH17(B) BH16(B) BH30 BH25 BH23(B) BH21(B) BH22(B) BH24 BH26 BH1(C) MW07 04 MW17 02 MW07 01 MW MW BH35 MW17 03 MW MW BH10(A) BH32 BH31 TCE>6 µg/m 3 (Omnibus CL) BH33 MW BH34 MW BH9(A) MW BH7(B) MW MW MW EMW 1 BH8(B) MW EMW 2 TCE>15 µg/m 3 (Omnibus Parkade) BH6(B) BH02M BH06M BH01M
10 Case Study #3: Metals in Soil Impact of Omnibus: Additional delineation Zn & As (Current) Zn, Cr, & As (Current) Off site contamination Introduces at least three third parties Additional CoCs BH3(B) BH115(A) BH115(B) BH21(A) BH6(C) BH4(C) BH12(A) MW BH11(A) BH17(A) BH20(A) BH19(A) BH18(A) BH5(C) BH13 BH14(A) BH23(A) BH22(A) VW BH3(A) MW BH2(B) BH16(A) BH15(A) BH4(B) BH2(C) BH5(D) MW BH10(B) BH4(D) BH8(C) MW BH1(D) BH2(D) BH7(C) BH11(B) BH20(B) BH14(B) BH3(C) MW BH6(D) BH12(B) BH9(B) BH15(B) BH19(B) BH18(B) BH17(B) BH16(B) BH30 BH25 BH23(B) BH21(B) BH22(B) BH24 BH26 BH1(C) MW07 04 MW17 02 MW07 01 MW17 03 MW MW EMW 1 MW BH7(B) MW Be (Current) BH8(B) MW EMW 2 BH6(B) Increased volume of soil $60/tonne = ~ extra $1.9M MW BH1(B) MW MW Elimination of Schedule 7 may provide some relief MW MW MW MW Zn, As, Cd, Cr, Ni, Cu, V, Se (Omnibus) As, Cr, Cu (Omnibus) BH02M BH35 BH10(A) BH32 BH31 BH06M BH33 BH01M BH34 MW BH9(A)
11 Case Study #3: Metals in Groundwater Impact of Omnibus: Off site: Introduces a third party Additional CoC Additional delineation and more metal contaminants Chromium speciation becomes driver Marine AW drops from ppb BH3(B) BH115(A) BH115(B) MW BH21(A) BH6(C) BH4(C) BH12(A) MW BH11(A) BH17(A) BH20(A) BH19(A) BH18(A) BH5(C) BH13 MW BH14(A) BH23(A) BH22(A) VW BH3(A) MW BH2(B) BH16(A) BH15(A) BH4(B) BH2(C) BH1(B) BH5(D) MW BH10(B) BH4(D) BH8(C) MW BH1(D) BH2(D) BH7(C) BH11(B) BH20(B) BH14(B) BH3(C) MW BH6(D) BH12(B) BH9(B) BH15(B) BH19(B) BH18(B) BH17(B) BH16(B) BH30 BH25 BH23(B) BH21(B) BH22(B) BH24 BH26 BH1(C) MW07 04 MW17 02 MW07 01 MW MW17 03 MW Zn, Cr, Pb, Cd Ni, Co (Omnibus) MW MW MW MW BH7(B) MW MW Zn, Pb, Cd, Ni, Co (Current) MW EMW 1 BH8(B) MW EMW 2 Cr (Omnibus) BH6(B) BH35 BH10(A) BH32 BH33 BH34 BH9(A) BH31 MW BH02M BH06M BH01M
12 Omnibus Review Key Takeaways Omnibus is effective November 1, 2017 Petroleum Hydrocarbons Minimal impact on newer releases Slight relaxation on older releases Status quo for vapours (except for parkades) Solvents Generally Positive effect Soil relaxed under DW scenario = cost savings for delineation and disposal costs Status quo for groundwater Relaxation of vapour standards (especially for parkades) Metals Generally negative effect Significantly more stringent soil standards = $$$ for delineation and soil disposal More groundwater migration and risk assessment A simplified soil relocation process may provide some relief
13 Special thanks to: for analytical results and soil disposal rates. Thank you. Questions Hemmera Envirochem Inc. 18 th Floor, 4730 Kingsway Burnaby, BC V5H 0C6
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