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0 <br /> LFR Inc. <br /> east of MW-012A, further indicate that reductive dechlorination is continuing past cis- <br /> ' 1,2-DCE and vinyl chloride. <br /> The groundwater results for the 13 wells sampled in the B-zone aquifer during the <br /> December 2006 event indicated that cis-1,2-DCE was detected in 6 of the 13 <br /> groundwater samples. The cis-1,2-DCE concentrations ranged from 0.73 µg/1 in MW- <br /> 20313-1 to 18 µg/1 in MW-20913, with the exception of MW-205B and MW-207B, <br /> which had detected concentrations of 1,000 µg/1 and 550 µg/1, respectively. These two <br /> samples with detected cis-1,2-DCE concentrations also have detected PCE and TCE <br /> concentrations that are on the same order of magnitude. <br /> As documented in the previous section, four groundwater samples were recently <br /> collected and analyzed for the full suite of geochemical parameters. Ethane and ethene <br /> concentrations were detected at the highest concentrations in groundwater from B-zone <br /> wells MW-205B (ethane: 3.8 µg/l and ethene: 0.28 µg/1) and MW-020B (ethane: 0.16 <br /> µg/l and ethene: 0.12 µg/1). Ethane was not detected in wells MW-108A and MW-208B <br /> (<0.025 µg/1), located in the proposed ERD treatment zone and downgradient. Ethene <br /> was detected in wells MW-108A and MW-208B at concentrations of 0.029 µg/l and <br /> 0.038 µg/I, respectively. The presence of ethane and ethene within the three B-zone <br /> wells indicates that active and complete anaerobic reductive dechlorination is occurring. <br /> The presence of ethene and hydrogen within A-zone well MW-108A indicates that <br /> conditions may be favorable for anaerobic degradations but that adequate food source <br /> may not be available. Thus, with the injection of a substrate, the A zone should respond <br /> favorably to ERD. <br /> 3.4 ERD Substrate Selection <br /> LFR has implemented ERD remedies under a variety of hydrogeological and <br /> geochemical conditions. LFR personnel have experience with ERD products that have <br /> specifically been designed for this purpose, including HRC from Regenesis, Emulsified <br /> Oil Solution (EOS) from EOS Remediation, Inc., CAPI8TM from DBI Remediation <br /> Products, and Adventus' EHC product. Additionally, LFR has successfully used <br /> industrial and food-grade products, including ethanol, sodium and potassium lactate, <br /> cheese whey, molasses, and others, to promote biologically favorable anaerobic <br /> reducing environments to support ERD. All of these substrates have been shown to be <br /> effective in creating anaerobic environments within groundwater and stimulating the <br /> growth of microorganisms ultimately responsible for the dechlorination of PCE to <br /> innocuous end products. While many of these substrates would likely be effective in <br /> treating the core of the Lincoln Center plume, LFR sought to identify the best product <br /> to achieve project goals. <br /> 3.4.1 Substrate Suitability <br /> A central feature of the Phase V IRA ERD injection is the installation of 22 injection <br /> wells to depths of 65 to 80 feet bgs, with the goal of providing a large amount of <br /> Page 14 wp-PM1V_IRA-Sep07-Final-06750.dm:lfr <br />