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concentrations are associated with the area that was over-excavated contained temporary <br /> piezometers PZ1B and PZ2B with 1,800 ug/L and 32 ug/L Benzene respectively on <br /> January31, 2003 Newly installed excavation monitor well MW10 contains 1200 ug/L <br /> MTBE <br /> FIGURE 7A <br /> Figure 7A represents the MtBE groundwater in the A zone along with the plume beneath <br /> CCFF The Sanchez plume is elongated extending west of the over-excavated area <br /> (MW10) out to "Geoprobe" hole P9 were degradation has left only minor TPHg (470 <br /> ug/L), Toluene (0 65 ug/L) and tert-Butanol (11 ug/L), the degradation byproduct of <br /> MTBE Highest concentrations of MtBE are associated with the areas north and west of <br /> MW10 The excavated area (MW10) formerly contained temporary piezometers PZ1A <br /> and PZ2A (highest concentration of MtBE 420 ug/L and 72 ug/L respectively on January <br /> 31, 2003) The MW 10 area has since reduced to 11 ug/L Newly installed downgradlent <br /> well MW9A is below laboratory lower detection limits <br /> The CCFF TPHg plume is associated with wells MW1 and MW3 and shows a connection <br /> to the Sanchez plume <br /> . FIGURE 713 <br /> Figure 7B represents the MtBE plume in the B zone Figure 7B resembles figure 7A with <br /> the only difference being an increase in MtBE found at wells 6B and 8B Historic water <br /> samples obtained from piezometers PZ1B and PZ2B contained 78 and 21 ug/L <br /> respectively <br /> TBA <br /> FIGURE 8A <br /> Figure 8A represents the TBA plume in the A zone TBA is only evident in well MW6A <br /> at 9 6 ug/L Historically TBA was detected in "Geoprobe" holes P8 and P10 at 11 and 6 <br /> ug/L respectively (February 2001) <br /> FIGURE 8B <br /> Figure 813 represents the TBA plume in the B zone TBA is only evident in wells MW6B <br /> and 8B at 12 ug/L <br /> Figure 9 illustrates the subsurface lithology and the extent of the A and B zones <br /> groundwater plumes within the A and B zones <br /> 7 Sanchez QM 1 st 2005 <br />