Laserfiche WebLink
• <br /> the soil sample collected beneath the diesel f iei dispenser The highest TPHg concentration <br /> detected was 4,800 mg/kg in the soil sample collected beneath the gasoline USTs Benzene was <br /> detected at concentrations up to 4 2 and 6 4 mg/kg in the soil samples collected beneath the USTs <br /> and dispensers, respectively Methyl tertiary butyl ether (MTBE) was detected at concentrations <br /> up to 28 and 18 mg/kg in the soil samples collected beneath the USTs and dispensers, <br /> respectively Approximately 400 cubic yards of soil excavated during UST and associated <br /> pipeline removal were disposed of off-site at a licensed landfill GHH Engineering estimated the <br /> mass of residual gasoline at the site to be approximately 163 gallons per a Request for No Further <br /> Action report dated February 2000 <br /> GHH Engineering performed quarterly groundwater monitoring and sampling from July 1997 to <br /> September 2002 The historical groundwater gradient direction has ranged from northeast to the <br /> southeast <br /> GROUNDWATER MONITORING <br /> Water level measurements were collected from wells MW-1P through MW-6P, MW-1 and MW-2 <br /> on August 11, 2004 The locations of the monitoring wells are shown on Figures 2 and 3 Depth <br /> to water levels ranged from 63 89 to 65 35 feet below the tops of the well casings The <br /> groundwater elevation decreased an average of 121 feet since the previous quarter The water <br /> level data were used to develop the groundwater elevation contour map (Figure 3) The average <br /> hydraulic gradient on August 11, 2004 was calculated to be 0 003 ft/ft or approximately 16 <br /> ft/mile, and flowed generally towards the south A summary of groundwater monitoring data is <br /> presented in Table 1 <br /> SAMPLING ACTIVITIES <br /> On August 11, 2004, ATC personnel collected groundwater samples from monitoring wells MW- <br /> 1P through MW-6P, MW-1, and MW-2 Prior to collection of groundwater samples, the depth to <br /> water was measured in the wells and the pH, electrical conductivity, and temperature were <br /> measured in the groundwater purged from the monitoring wells and recorded Aquifer <br /> parameters were allowed to stabilize and a minimum of three well casing volumes were purged <br /> from each well prior to sampling The wells were allowed to recover and samples were collected <br /> from each well using dedicated disposable bailers Purged well water was contained on site in <br /> DOT approved 55-gallon drums for disposal pending receipt of laboratory results <br /> The groundwater samples collected from each well were submitted to Argon Laboratories, a <br /> state-certified analytical laboratory (Environmental Laboratory Accreditation Program Certificate <br /> No 2359) located in Ceres, California, for analyses Laboratory analyses consisted of TPHg <br /> utilizing EPA Method 8015B, BTEX utilizing EPA Method 8021B, and oxygenate fuel additives <br /> MTBE, ethyl tertiary butyl ether (ETBE), di-isopropyl ether (DIPE), tertiary butyl alcohol (TBA), <br /> tertiary amyl ether (TAME), 1,2-dichloroethane (1,2-DCA), and 1,2-dtbromoethane (EDB) <br /> s lenvironmental12591210003-Stockton\Quwtly\3QR 2004 doc 2 <br />