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' 0 0 <br /> ' 2.0 NATURE, SOURCE, AND EXTENT OF CHEMICALS OF CONCERN <br /> Potential contaminants onsite are associated with use of the Site as a firing range. Field <br /> investigation activities completed September 11 and 14, 2015 by Geocon included: <br /> ' ➢ Three direct push soil borings to 20 to 25 feet including collection of soil and grab <br /> groundwater samples <br /> ➢ Collection of XRF surface lead readings at 152 discrete locations <br /> ' ➢ Collection of soil samples at 27 of the 152 discrete locations to confirm XRF readings <br /> ➢ Excavation of seven trenches in the primary impact berm and side berms <br /> ➢ Metal detecting to determine depth of bullet penetration in the impact berm <br /> ' The following laboratory analyses were performed as part of the site investigation: <br /> t ➢ Four soil samples for CAM 17 metals by EPA 601013/7471 <br /> ➢ 44 soil samples for total lead by EPA 6010B <br /> ➢ Six soil samples for WET soluble lead by EPA 7420 <br /> ➢ 13 soil samples for TCLP soluble lead by EPA 1311 <br /> ' ➢ One groundwater sample for CAM 17 dissolved metals by EPA Test Methods <br /> 601013/7470A <br /> ' ➢ Two groundwater samples for dissolved lead by EPA 6010B <br /> Total lead concentrations in soil samples collected from a depth of one foot or greater ranged <br /> ' from<1 to 31 mg/kg. Total lead concentrations in surface soil ranged from 7.9 to 42,000 mg/kg; <br /> soluble WET lead concentrations ranged from 3.7 to 1,100 mg/l; and, soluble TCLP lead <br /> concentrations ranged from 0.29 to 1,400 mg/l. Other metals were detected in soil including <br /> ' antimony, arsenic, barium, copper, vanadium, and zinc. Other metal concentrations were below <br /> 2016 Residential USEPA Regional Screening Levels (RSLs) except antimony and arsenic <br /> ' (residential RSLs of 31 and 0.68 mg/kg, respectively) detected at maximum concentrations of <br /> 300 and 81 mg/kg,respectively (USEPA 2016). It is also noted that the detection limit for <br /> cadmium (<20 to <100 mg/kg), cobalt (<20 to <100 mg/kg), and thallium (<20 to <100 mg/kg) <br /> ' exceeded the residential RSLs of 71, 23. and 0.78 mg/kg, respectively. <br /> Antimony and arsenic concentrations exceeding RSLs were co-located with elevated lead <br /> ' concentrations suggesting lead is the metal driving remedial operations. Analysis of a select <br /> number of confirmation samples for CAM metals is proposed to a) confirm the observed <br /> correlation between antimony, lead, and arsenic concentrations in the site assessment data and b) <br /> to confirm that cadmium, cobalt, and thallium concentrations are below their respective RSLs. <br /> All dissolved metal concentrations in groundwater were either below laboratory reporting limits <br /> ' or were below respective Maximum Contaminant Levels (MCLS). <br /> Geocon sample locations and results for the XRF samples and the soil and groundwater samples <br /> are included on Geocon's Tables 1 through 4 included in Appendix B. <br /> tA statistical analysis was conducted by Geocon to evaluate the correlation between 1) XRF <br /> readings and laboratory analytical results for total lead, 2) total and WET lead concentrations, <br /> PnciFicEDGE ENcweeawc 4 SREW_Manteca_draft.docx <br /> ' (949)470-1937;(949)470-0943(FAX) <br />