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29 January 2002 <br /> ' AGE-NC Project No, 98-0466 <br /> Page 8 of 25 <br /> ' The metals lead, zinc and chromium were reported to be within bac ound concentrations, but <br /> formaldehyde was detected at concentrations of 26 mg/kg and 43 mg1g. Kleinfelder believed the <br /> formaldehyde results to be false positives. AGE does not have a copy c f the assessment report. <br /> ' In the AGE-prepared Phase II Site Assessment Report- Septic Leach Kelds and Drainage Ditch, <br /> ' dated 26 October 2000, AGE reported the analytical results from soil and ground water samples <br /> collected from the septic tank leach field west of the Millworks buil ' g. One grab ground water <br /> sample was collected at a depth of approximately 40 feet bsg (LP4). TRPH was detected at a <br /> concentration of 15 milligrams per liter (mg/1). Total chromium was de ected at a concentration of <br /> 1.17 mg/l. The sample was not analyzed for dissolved chromium Lead was detected in the ground <br /> water sample at 0.10 mg/1. The sample was not filtered prior to analysis, io the metals results include, <br /> ' total metals from entrained mineral grains and are not representative of dissolved metals <br /> concentrations. <br /> ' Neither PCP nor TCP were detected in the groundwater sample. Zinc concentrations in the ground <br /> water sample did not exceed environmental guidelines. Formaldehy at 4.7 mg/l exceeded the <br /> Action Level of 0.1 mg/1 in the ground water sample. Table 7 and E shows the analytical data <br /> obtained from the October 2000 samples, Figure 4 shows the sample localities. <br /> ' 2.3.3. Maintenance Building Septic Leach Field-Active <br /> On 05 December 2000, AGE collected soil and grab ground water samples from the septic leach <br /> ' field east of the active maintenance building located on the northern portion of the property. <br /> Analyzed samples did not contain detectable concentrations of TRPH, formaldehyde, TCP, TCE or <br /> PCP. Concentrations of metals, including chromium, lead and zinc were all within background <br /> ' values for soil samples. Concentrations of metals in ground water sam les were above MCLS and <br /> PRGs for tap water for each metal analyte;however,the groundwater samples were not filtered prior <br /> to analysis, so the metals results include total metals from entrained mineral grains and are not <br /> representative of dissolved metals concentrations. Tables 7 and 8 show the analytical data obtained <br /> from the December 2000 samples. AGE believes the area to have been misidentified as a potential <br /> ' receptor of contaminants (See Site Environmental History, dated 04 May2001, discussion of septic <br /> tanks) and that the area has been adequately assessed. <br /> ' 2.4. WASH-DOWN AREAS <br /> According to Kleinfelder (1992), rinse water generated during cleaning of glue application <br /> equipment, priming equipment and saw blades was discharged onto surface soils at five separate <br /> locations at the site. The areas considered by Kleinfelder (1987), baied on the D&M Phase II <br /> ' Investigation (1987) report, as having potential contamination were located east of the Ray Bond <br /> Advanced GeeBnvlron tal,Inc. <br />