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Al Jesena - 5 - 1 March 200;) <br /> Draft RI for OU#3 <br /> NCTS, Stockton <br /> (Metcalf, 1962). Moreover, chlorinated contaminants (i.e., pesticides, PCBs), as well as organic <br /> carriers/solvents used in the distribution of the products show peaks on a chromatogram that are similar <br /> to TPH-diesel. <br /> Based on communications with the San Joaquin County Agricultural Commissioner's Office, diesel oil <br /> was used as a carrier to DDT for weed control. Lightweight Superior brand oil was also used as a <br /> solvent for the DDT that came in powder form. A Senior Agricultural Biologist, who worked on the <br /> island in 1968 and then regulated the island between 1970 and 1985, stated that the Navy was known to <br /> dump crankcase oil, solvent from cleaning ships, and other waste oil/fuel in the landfill area. The <br /> biologist stated that you could smell the petroleum hydrocarbons when driving through the landfill area. <br /> According to the San Joaquin County Mosquito Abatement Agency, they performed surveillance <br /> activities on the island, as well as lab work to identify mosquitoes for the Navy. The Agency <br /> representative stated that #2 diesel oil was used as a larvacide and Weed Oil along the ditches for weed <br /> control. <br /> The RI reports WET data results depicting Total Petroleum Hydrocarbons and Total Petroleum <br /> Extractable Hydrocarbons (Table K) as Nonpetroleum Hydrocarbons, Motor Oil Range Organics, Diesel <br /> Range Organics, and Gasoline Range Organics. In order to verify this phenomenon, we request the <br /> Navy submit fingerprinting chromatograms of representative soil samples from the site and standard <br /> diesel, gasoline, and motor range chromatograms for comparison. The chromatograms must be <br /> produced at similar scales and a reasonable scale to clearly define peaks. The chromatograms must be <br /> signed by the chemist who interpreted the data. <br /> Based on our research, we believe that the petroleum hydrocarbons found in the landfill area resulted <br /> from historic weed control and pest abatement by the Navy. Therefore, the Navy should determine the <br /> extent of this contamination and propose remedial alternatives for these COCs in the feasibility study. <br /> Landfill Management Approach <br /> The Navy continues to use the term"presumptive remedy"during the SAP and RI phase of the <br /> investigation. Again, we reiterate that presumptive remedies may not meet the technologic and/or <br /> economic objectives towards cleaning up sediment, soil, surface water and groundwater at OU #3 <br /> landfill sites. As before, excavation and removal of waste, especially hazardous waste, to off-site <br /> disposal areas should be an alternative. Capping may be an alternative at sites that are above the highest <br /> groundwater level and are shown to be a threat to surface water or other environmental factors,but not <br /> necessarily for sites that are partially inundated with groundwater. Containing groundwater contaminant <br /> plumes may be an option once hot spots have been remediated using best available technology(BAT). <br /> Without knowing the content or volatility of the waste within each trench,we cannot presume to know <br /> what potential threat or nuisance the waste may pose in the future. Containers may deteriorate and leach <br /> toxic materials and/or mixed waste may physically/chemically react and potentially pose a threat to the <br /> environment. Therefore,waste characterization is critical in determining what remedial options are <br /> viable. These issues were discussed in the development of the SAP and must be resolved during the <br /> remedial investigation phase. <br />