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• <br /> Draft Soils FS Report Memorandum -4- 17 April 1992 <br /> DDRW, Sharpe <br /> detail in the memorandum on the pilot VES. In addition, the two USTs which <br /> contained waste solvents appear to have been inadequately investigated and need <br /> additional investigation to determine if soils and ground water are <br /> contaminated in the surrounding areas of the USTs. Finally, it is unclear why <br /> only two soil sites have been identified as needing remediation when there are <br /> more than two distinct VOC plumes. <br /> 10. Remediation by capping is proposed for some areas with lead contaminated soils. <br /> Capping of the lead contaminated soils is unacceptable based on the existing <br /> data base. Because the solubility of the lead in the contaminated soils is <br /> unknown and because the ground water is relatively shallow ground water (and <br /> may be less than five feet depending on the depth of the WMU or UST) , capping <br /> of the contaminated soils may be inadequate to protect ground water quality. <br /> Ground water could continue to be degraded if the unsaturated zone is thin, the <br /> lead is soluble and ground water levels fluctuate. Additional information on <br /> the solubility of lead, the thickness of the unsaturated zone beneath the WMU <br /> or UST and the historical high ground water elevation is needed to determine if <br /> capping is an acceptable remedial alternative. Chapter 15 of the California <br /> Code of Regulations (CCR) must be complied with if any soil contamination is <br /> left in-place and may degrade water quality. <br /> 11 . Many of the state Applicable or Relevant and Appropriate Requirements (ARARs) <br /> were not identified in the Draft Soils FS Report. Of particular concern, is <br /> that Chapter 15, Division 3, Title 23 of the Water Code was not identified. <br /> This promulgated ARAR has location, action and chemical specific requirements <br /> for waste discharges to land. The WMUs (sump at Building S-119) which contain <br /> hazardous waste constituents are subject to the Toxic Pits Cleanup Act (TPCA) <br /> if the hazardous wastes were stored in the sump after 1 January 1985. The <br /> requirements of the TPCA must be considered as an ARAR. In addition, the <br /> requirements of Chapter 16 of the CCR must be complied with for fuel USTs. The <br /> FS Report needs to be revised to include these ARARs. We have enclosed a table <br /> which identifies our ARARs. More specific ARARs will be provided as remedial <br /> measures are developed. <br /> SPECIFIC COMMENTS <br /> a. Depth of Soil Borings. The depth of many of the soil borings extended only to <br /> 15 feet below ground surface (bgs) . It is unclear whether the borings extended <br /> to the ground water table. In addition, in some of the borings (S13-B2 at <br /> Building 391, PS7-B1 at Buildings T-661 and 669) , the contaminant <br /> concentrations were found to be the highest of the deepest soil samples. If <br /> the ground water table is greater than 15 feet bgs, it is possible that the <br /> contaminant concentrations further increase downward in the unsaturated zone. <br /> The vertical extent of contamination in the unsaturated zone needs to be <br /> defined for each constituent of concern. <br /> b. Composite Soil Samples. The soils boring samples and surface samples were <br /> frequently composited over depth. The contaminant concentrations in composite <br /> samples are generally less than for grab samples. Because composite samples <br /> were collected over five foot intervals in the soil borings, estimates of total <br /> contaminated soil are affected which would lead to over or under estimates of <br /> the volume of soils above cleanup levels needing remediation. <br />