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N%Tc <br /> 1117 Lone Paim Avenue, Suite Modesto, CA 953511 <br /> www.atcassociates.com <br /> 209-579-2221 <br /> ' ASS O C I ATE S I N C . <br /> Fax 209-579-2225 <br /> Environmental, Geotechnical and Materials Engineers <br /> of benzene, 3 ,600 micrograms per liter (gg/L) and 2,600 gg/L, were detected in the groundwater <br /> samples collected from MWl and MW8 , respectively. TPHg was detected in the groundwater <br /> samples collected from MWl , MW2, MW3 , MW5 , MW6, MW8 , and MW9 . The highest <br /> concentrations of TPHg, 120,000 µg/L and 53 ,000 pg/L, were detected in the groundwater <br /> samples collected from MWl and MW8 , respectively. MTBE was detected in the groundwater <br /> samples collected from MW2 and MW3 at concentrations of 19 gg/L and 19 lig/L, respectively. <br /> 1 ,2-DCA was detected in the groundwater samples collected from MWl through MW6, MW8, <br /> MW9 , and MW12 at concentrations ranging from 1 . 1 µg/L to 540 µg/L. The highest <br /> concentration of 1 ,2-DCA was detected in the groundwater sample collected from MW3 . TBA <br /> was detected in the groundwater samples collected from MW2 and MW3 at concentrations of 47 <br /> µg/L and 29 µg/L, respectively. Analytical results of groundwater samples are summarized in <br /> Table 3 . Laboratory data sheets and chain-of-custody documentation are contained in Appendix <br /> E. Isoconcentration maps depicting benzene, MTBE, and 1 ,2-DCA concentrations in the <br /> groundwater samples collected from the shallow zone during the fourth quarter of 2006 are <br /> shown on Figures 6, 7, and 8 , respectively. Isoconcentration maps depicting benzene and 1 ,2- <br /> DCA concentrations in the groundwater samples collected from the intermediate zone during the <br /> fourth quarter of 2006 are shown on Figures 9 and 10, respectively. <br /> 5.0 CONCLUSIONS <br /> The laboratory analytical results of groundwater samples collected from the monitoring wells in <br /> November 2006 indicate the lateral extent of petroleum impacted groundwater in the shallow <br /> zone appears to be defined in all directions except to the south. MTBE was detected in the <br /> groundwater sample collected from MW3 and 1 ,2-DCA was detected in the groundwater samples <br /> collected from MW3 and MW9 . These wells are located in the southern portion of the site. <br /> Monitoring wells MW 1 and MW8 continue to be the most impacted wells . <br /> The lateral extent of petroleum impacted groundwater in the intermediate zone is not well <br /> defined. The apparent groundwater flow direction in the intermediate zone as indicated by depth <br /> to water measurements collected on December 7, 2006, is to the north. This flow direction is <br /> inconsistent with historical data that generally indicates a southerly groundwater flow direction in <br /> this zone. Monitoring wells MW4 and MW12 are slightly impacted, and MW5 and MW6 <br /> continue to be the most impacted wells. <br /> Petroleum - hydrocarbon have not been detected in groundwater samples collected from MW7 <br /> locate�a +a the former source area since December 20055 and were not detected in the groundwater <br /> sample collected from MW15 located in the southern portion of the site and potentially <br /> downgradient of the former source area. Monitoring wells MW7 and MW15 are screened from <br /> approximately 116 to 121 feet bgs and 141 to 151 feet bgs, respectively. The laboratory data <br /> associated with groundwater samples collected from these wells indicates the vertical extent of <br /> petroleum contamination in groundwater lies between 90 and 116 feet bgs. <br /> Si\Env iromcntal\28349treports\sum.doc 6 ATC Associates Inc. <br />