Laserfiche WebLink
and Nilsen, 1990). Data from nearby studies within the Port area indicate a soil profile to a <br /> depth of about 20 feet bgs comprised of interbedded sands and clays, mostly under reduced <br /> conditions°(Sierra-Pacific Groundwater Consultants [SPGC], 1994). Lithologic data from <br /> boring B5-1 (Appendix A) indicate the lithology in the vicinity of the former USTs comprises <br /> mostly fine- to very fine-grained sand and silty sand to a depth of about 17 feet bgs, with silt <br /> and clay predominate from about 17 to 28 feet bgs, the maximum depth explored at the site. <br /> Soils encountered near the former dispenser area (borings.B5-4 and B5-5) comprise mostly <br /> clay. A 1- to 2-foot thick bed of sand occurs beneath the former dispenser area at about 17 <br /> feet bgs (Appendix A). <br /> Data from nearby studies indicate that the current depth to groundwater in the vicinity ranges <br /> from about 5 to 10 feet bgs (SPGC, 1998, and EMCON, 1998). Seasonal fluctuations in the <br /> water table appear to range from about 3 to 5 feet, with some as much as 6 to 9 feet. Tank <br /> removal inspection records for this and other Port sites (dating back to 1987) indicate that no <br /> groundwater was encountered during excavation of tanks or soil resampling to a depth of as <br /> much as 16 feet bgs. Water levels in this area have risen as much as 8 feet since 1994, 2 to <br /> 3 feet of which appear to be attributable to the heavy and prolonged El Nino rainfall events of <br /> last winter. The static water level in the borings emplaced near the former USTs (borings B5-1 <br /> to -3) was,'about 9 feet bgs on August 5, while water levels in the borings emplaced near the <br /> former dispenser area (borings B5-4 and -5) were about 1l.feet bgs (Appendix A). Based on <br /> nearby studies (SPGC, 1998, and EMCON, 1998) groundwater flow directions in the vicinity <br /> appear to be variable, ranging from west northwest to east southeast. Flow direction changes <br /> may be due to tidal influences produced by the deep water channel to the north and the San ` <br /> Joaquin River to the west and southwest of the Port area. <br /> 4.2 SOIL AND GROUNDWATER ANALYTICAL RESULTS <br /> Analytical results for soil and groundwater samples collected during this investigation are <br /> presented on Table 2. The laboratory data sheets and chain-of-custody records are included <br /> in Appendix B. No PHCs were detected in soil samples collected near the former USTs in <br /> borings B5-1 through B5-3. However, the groundwater sample collected from boring B5-1, <br /> along the eastern side of the former UST excavation, contained BTEX constituents and 4.2 I <br /> mg/f TPHg. Trace amounts of benzene (0.005 mg/kg) and toluene (up to 0.015 mg/kg) were <br /> detected in soil samples collected in boring B5-5 near the former dispenser area. No PHCs <br /> were detected in the soil samples collected in boring B5-4. However, groundwater in the f <br /> vicinity of the former dispenser is impacted with PHCs. Groundwater samples collected from <br /> borings B5-4 and B5-5 contained BTEX constituents (up to 0.46 mg/f xylenes and 0.035 mg/f <br /> benzene) and up to 1.1 mg/P.TPHg. The laboratory included a note on the analytical results <br /> for water samples W-007 and W-008, collected from boring B5-4, stating "Chromatography 1 <br /> 6 "117WgVRPrSWUSTMV.RPr <br />