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10 May 1999 <br /> S AGE-NC Project No 95-0111 <br /> Page 4 of 6 <br /> 31 STRATIGRAPHY <br /> Tan silty clay and utility backfill were encountered in the investigation area Sitty clay was <br /> distributed from the surface to 15 feet bsg in soil boring MW7 Silty clay was distributed from the <br /> surface to 10 feet bsg in soil boring MW8 and pea gravel was encountered from approximately 10 <br /> feet bsg to above 15 feet bsg The gravel was underlain by silty clay to the total depth of the soil <br /> boring at 15 feet bsg A stratigraphic cross section of the soil at the site is depicted in Figure 3 <br /> 3 2 LABORATORY RESULTS OF SOIL SAMPLES <br /> TPH-g was detected in one of the six soil samples analyzed TPH-g was detected at a concentration <br /> of 5 7 milligrams per kilogram(mg/kg)in soil sample BMW7-10 Xylene was detected in the same <br /> soil sample at a concentration of 0 015 mg/kg <br /> Soil samples collected and analyzed from depths of five feet and ten feet bsg in the same boring had <br /> detectable TPH-d at concentrations of 16 mg/kg and 3 0 mg/kg, while the soil sample from a depth <br /> Iof 15 feet bsg had no detectable petroleum impact <br /> TPH-d was detected in the soil analyzed from boring B-VIW8 at a depth of ten feet bsg at a <br /> I concentration of 140 mg/kg, while TPH-d was not detected in the soil from a depth of 15 feet bsg <br /> in the same soil boring Oxygenated compounds were not detected in the soil samples analyzed <br /> Analytical results of soil samples are summarized in Tables 1 and 2 <br /> The laboratory report (MAI Laboratory ID 02111 through 02116), quality assurance and quality <br /> control (QA/QC)reports and chain-of-custody form are in Appendix C <br /> I <br /> 3 3 GROUND WATER FLOW DIRECTION AND GRADIENT <br /> I <br /> The relative ground water elevation in each well was calculated by subtracting the depth to ground <br /> I water from the surveyed relative casing elevations The depths to ground water and relative ground <br /> water elevations are tabulated in Table 3 All existing wells were surveyed relative to the casing of <br /> monitoring well MW-1,which had been assigned an arbitrary casing elevation of 20 feet The depth <br /> I to ground water ranged from 6 30 feet below the well casing (bwc) in MW-4 to 9 50 feet bwc in <br /> MW-1 <br /> The relative ground water elevation at the site ranged from 10 21 feet in MW-5 to 11 57 feet in MW- <br /> 6 The relative ground water elevation increased an average of 0 33 feet over the last quarter The <br /> inferred ground water flow direction at the site was towards the northeast, consistent with results <br />' Advanced GeoEnvironmental Inc. <br /> I <br />