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r . Mr. Robert McClellon <br /> February 9, 2006 <br /> Page 3 of 4 <br /> • which above the California-modified residential PRG of 150 mg/kg. Due to this initial result, the <br /> sample was also analyzed for soluble lead by EPA Method WET/7420 (STLC) and EPA 1311/7420 <br /> (TCLP). The results indicated STLC lead at '15 mg/L and TCLP lead at 8.4 mg/L, which exceed <br /> both California and Federal RCRA hazardous waste critera (5 mg/L). For specific metals results <br /> please see Table 1. <br /> WASTE DISPOSAL <br /> The analytical results of waste characterization sampling conducted at the site indicate that the soil/ash <br /> waste generated from the September 30, 2005 excavation activities should be considered a Federal <br /> (RCRA) hazardous waste. Approximately 110 tons of waste will require disposal. Mr. Palomino has <br /> submitted a Notice of Regulated Waste Activity with the US EPA Region 9 RCRA Notifications Unit <br /> to obtain a generator's identification number so that he can transport the waste to Kettleman Hills <br /> Class I landfill for disposal. <br /> EHD will be notified at least 48 hours prior to transporting the waste off site under hazardous waste <br /> manifest. <br /> • PROPOSED ADDITIONAL EXCAVATION ACTIVITIES <br /> Mr. Palomino would like to continue to make progress toward site cleanup and proposes the following <br /> activities to that end: <br /> 1. Relocate the stockpiled hazardous waste from its current location approximately 20 feet east and <br /> remove the inert debris (concrete, timber, etc.) in preparation for disposal (Figure 2). The waste <br /> will be moved by individuals that have current certification in hazardous waste operations <br /> (HAZWOPER) pursuant to 29 CFR 1910.120(e) using a Case 580 backhoe or Caterpiller 977C <br /> bulldozer. The material will be placed on 6-mil plastic sheeting and will be covered by plastic <br /> when not being sorted. <br /> 2. Continue excavation activites in the southwest corner of the site where a debrisibum pit has been <br /> previously identified and move the existing soil stockpile in that location approximately 100 feet to <br /> the north (Figure 2). The existing pile and excavated material will be placed on trucks and <br /> stockpiled approximatey 100 feet north of the current location. The material will be placed on and <br /> covered with 6-mil plastic sheeting. Upon completion of the excavation, characterization soil <br /> samples will be collected at the rate of one 4:1 composite sample for every 250 cubic yards of <br /> stockpiled material. The samples will be analyzed for TPHd, TPHg, VOCs, SVOCs, PCBs, and <br /> CAM 17 metals by appropriate analytical methods. <br /> Site activities will be conducted pursuant to the procedures and safety protocols outlined in the <br /> • September 22, 2004 Workplan for Site Mitigation and the December 17, 2004 Addendum. In general <br /> safety procedures will include the following: <br /> G:\GROUNDZE\Palomino\soilpileresult2—wp.doc <br />