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LW <br /> bioremediation is probably the predominant bioremediation occurring in the contaminant <br /> plume. Thus, it appears that nitrate and sulfate are the primary electron acceptors in the <br /> `' groundwater beneath the site. Some studies say that benzene is not degraded when nitrate and <br /> sulfate are the electron acceptors, and other studies say that benzene can be degraded with <br /> �. these electron acceptors (Borden et al, 1995). However, nitrate and sulfate are known to aid <br /> in biodegradation of toluene, ethylbenzene and xylenes. <br /> z. <br /> Based upon geotechnical and geochemical data collected from groundwater and/or soil <br /> underlying the project site, this study concludes intrinsic bioremediation is taking place in the <br /> LM contaminantlume beneath the site. Biodegradation <br /> P g appears to be continuing in an aerobic and <br /> anaerobic environment. A review of groundwater chemical data suggests the contaminant <br /> &- plume is stable since it appears that petroleum hydrocarbon concentrations are decreasing in <br /> the wells. This can be verified with further groundwater monitoring at the site. <br /> LN <br /> Additional evidence of bioremediation occurring in groundwater under the site is found in the <br /> soil vapor analytical data. Carbon dioxide concentrations are higher in vapor samples from <br /> borings inside the plume than those outside the plume, suggesting bioremediation of the <br /> i petroleum hydrocarbons in the capillary fringe. Also, methane was detected in the soil vapor <br /> L.'__ sample from boring SB2, which is inside the plume, suggesting this is a byproduct of <br /> ' bioremediation of the petroleum hydrocarbons and floating product in the capillary fringe. <br /> 7.0 POTENTIAL RECEPTORS AND PATHWAYS <br /> 7.1 Potential Receptors <br /> At the request of the PHS/EHD, Smith Technology conducted a search of the Department of <br /> Water Resources (DWR) groundwater well construction logs to identify any groundwater wells <br /> located within one half mile of the site. The search revealed thirteen wells located in the <br /> vicinity of the site. Well logs for the on-site water supply well were not found in the DWR <br /> `' records. The well locations are shown on Figure 8. The wells were located on the map <br /> according to "well location" description information provided on the well construction logs. If <br /> +- the description was not helpful, the township, range, and section were used to locate the wells <br /> on the map. The well construction logs are contained in Appendix VI. <br /> The on-site.well is the closest to the plume (within approximately 100 feet of the plume). At <br /> the writing of this report, no data was able to be obtained from the property owner, tenant or <br /> { PHSIEHD concerning the well depth, screen interval or depth of seal. The petroleum affected <br /> w:1951221Plumerpt 15 <br /> LW <br /> • <br /> SMTH <br />