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Supplemental Investigation Report,Problem Assessment Report and Work Plan <br /> Clemua and Abatement Order No 5-00-707 EAI Proiect No 1232 <br /> • Unocal excavated approximately 6 000 cubic yards of impacted soil at its site in 1988 <br /> Pp Y � Y p , <br /> to a maximum depth of 53 feet bgs Through aeration, it was reported that the <br /> hydrocarbon concentrations in 5,800 cubic yards of the excavated soil were reduced to <br /> acceptable levels, and that 5,800 cubic yards of the excavated soil was reused on-site as <br /> backfill The remaining 200 cubic yards of excavated soil was transported off-site for <br /> processing <br /> • Significant ground water fluctuation, over 25 feet, has occurred beneath both the Wards <br /> and Unocal sites, which may have resulted in the formation of a smear zone <br /> 0 Vertical extend of ground water contamination has been observed to the maximum <br /> extent explored to date, i e , approximately 65 feet bgs <br /> a Highest historical concentrations of dissolved hydrocarbons were detected in former <br /> Unocal well MW-1 (see Figure 4 and Table 4) A building is currently located over the <br /> area where well MWA was formerly located The area between former Unocal well <br /> MWA and existing Unocal MW-11 is probably impacted with petroleum hydrocarbons <br /> Proposed wells MW-23S and MW-23D (see Section 5 1) will provide data on this <br /> supposition <br /> • Petroleum hydrocarbons were present in ground water samples collected from the RIW, <br /> when the RIW was in use <br /> a Ground water flow direction is to the east when the RIW is not used, and to the <br /> southwest when the RIW is in operation, <br /> o The area between the Unocal and Wards sites and the RIW is impacted with petroleum <br /> hydrocarbons The vertical extent of this impact is currently unknown Proposed CPT <br /> locations (see Section 5 2) will provide data on this issue <br /> a Based on available analytical data for the Wards site, dissolved hydrocarbons are <br /> subjected to biodegradation by natural microorganisms <br /> 63 1 Institutional Control <br /> Shut down of the existing RIW (this occurred on August 22, 2000) and relocation andro er <br /> p P <br /> construction of a new RIW is probably the most efficient effort which will meet the ultimate <br /> threshold criteria, such as overall protection of human health and environment and compliance <br /> with applicable regulatory guidance Based on the results of hydrogeological investigation <br /> completed by ERI (see ERI, 1999), the new RIW location should be at least 1000 feet from the <br /> existing RIW location Further, the new RIW must be properly constructed, e g, slots <br /> beginning at depths not less than 150 feet bgs, and zones properly sealed against pollution <br /> A separate Work Plan will be submitted to the RWQCB by November 6, 2000, addressing _ <br /> relocation of the RIW <br /> HS 1232P 1RW_WP -20^ <br /> ENVIRONMENTAL AUDl7,INC <br />