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advantage of reduced trucking costs. The estimated costs in Table 1 assume disposal at the Forward facility. i Forward has specified analytical requirements for profiling a waste. The soil at the site containing waste oil would require one 4-point composite sample be collected and analyzed for semivolatile organic compounds (EPA Method 8270), halogenated organic compounds (EPA Method 8010), the five TCL-P metals (cadmium, chromium, lead, nickel, and zinc), and a 96-hour Acute Aquatic LC5 fish bioassay. It is assumed that the results of these analyses will allow the material to be classified as a Class II waste and that the waste is non-hazardous. i Once the waste has been profiled and accepted by the landfill, then a front-loader will be mobilized to the site to load the affected soil into 18-cubic yard end-dump trucks. It is assumed that six trucks will each deliver three loads of soil to the landfill in a single day. Although the waste will not be a hazardous waste (unless analytical data from i profiling analyses indicates otherwise), an unofficial manifesting system will be used to track the shipment and receiving of the wastes to the landfill. i I 4.4 REFERENCES ICF Kaiser, "Quarterly Groundwater Monitoring Report and Results of Confirmation i Sampling of Soils Excavated from 425 North Union Street and Stockpiled at 1320 West k Weber Street. Former Union Ice facility 425 North Union Street, Stockton, California." October 4, 1995. t ICF Kaiser, "Remediation Workplan for Stockpiled Soil at the Union Ice Facility, 1320 West Weber Street, Stockton, California." December 22, 1995. State of California Leaking Underground Fuel Tank Task Force "Leaking Underground Fuel Talk Field Manual: Guidelines for Site Assessment, Cleanup, and Underground Storage Tank Closure." October, 1989. R41820A-0102960-3 soilrem2.pin 3 I r