Laserfiche WebLink
SEDC ® R <br /> SIECOR <br /> ' newly installed wells contained maximum concentrations of TPHgand MtBE of 72 00 <br /> 0 ,. <br /> ppb (MW-6) and 750 ppb (MW-6), respectively (IT, 2001). <br /> Between June 2002 and November 2002, SECOR performed three phases of off-site <br /> assessment at the site. The initial phase was conducted on June 5, 2002 and consisted <br /> ' of the advancement of five geoprobe borings (GP-1 through GP-5). Based on the soil <br /> and groundwater analytical results from GP-1 through GP-5, SECOR performed the <br /> second phase of offsite assessment on June 21, 2002. The second phase of off-site <br /> ' assessment consisted of four additional step-out geoprobe borings (GP-6 through GP- <br /> 9). The final phase of offsite assessment, conducted in November 2002, consisted of A <br /> ' the installation of six groundwater monitoring wells (MW-10 through MW-15) (SECOR, <br /> 2003). <br /> In October 2003, SECOR arranged to sample the Lathrop Grammar School irrigation <br />' well, located approximately 1,600 feet northeast of the site. This well was the closest of <br /> three wells identified during a 2000-foot radius receptor survey conducted at the site. <br /> The well is used to irrigate the grammar school and operates from 7:00 pm to 5:10 am. <br />' The well was sampled at 4:40 am (under supervision of Manteca Unified School District <br /> staff), near the end of the well pumping cycle. The water sample was collected from a <br /> spigot at the well head. The sample was analyzed for total petroleum hydrocarbons <br /> i calculated as gasoline (TPHg), benzene, toluene, eth (benzene <br /> Y , xylenes {BTEX <br /> compounds), and fuel oxygenates MtBE, EtBE, TAME, TBA, DIPE, EDB, 1,2-DCA, and <br /> ethanol by EPA Method 8260, single run. These constituents were reported as not ' <br />' detected (SECOR, 2003). <br /> In October 2003, SECOR conducted a study to determine if the Lathrop Grammar <br />' School irrigation well was affecting groundwater flow or gradient beneath the site. <br /> Groundwater transducers were placed in site wells and recorded groundwater `T <br /> elevations for 4 days. Based on data collected from the transducers, it was determined r <br /> n <br />' that the Lathrop Grammar School well was not influencing groundwater elevation and <br /> flow at the site (SECOR, 2003). <br /> 4.1 <br /> On June 12, 2004, SECOR supervised the advancement of five geoprobe borings (GP- <br /> 10 through GP-14). The purpose of the work was to delineate the lateral extent of ' <br /> petroleum hydrocarbon impact in soil and groundwater downgradient of the site, and to <br /> determine the placement of wells to complete delineation of the plume. Soil samples at <br /> 10 and 15 feet bgs from geoprobe borings GP-10 through GP-14 were collected and <br /> submitted for laboratory analysis. Soil samples were analyzed for TPHg, BTEX, and <br /> fuel oxygenates by EPA Method 8260B. TPHg, xylenes, and ethanol were reported in <br /> soil sample GP-13@10 at concentrations of 1.2 mg/kg, 0.0095 mg/kg, and 0.65 mg/kg, <br /> respectively. No detectable concentrations of petroleum hydrocarbons were reported in <br /> the soil samples from borings GP-10, GP-11, GP-12, and GP-14. Groundwater "grab" <br /> samples collected from each of the geoprobe boring locations were analyzed for TPHg, . <br /> q. <br /> BTEX, and fuel oxygenates by EPA Method 8260B. MtBE was reported at a <br /> 1205 SCMAOC 3 <br />