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' GeologualTeckiucrl Page 5 <br /> Groundwater Momtoring Report <br /> Project No 770 2 <br /> August 27,2004 <br /> ' other events all displayed an easterly trend to groundwater direction It is noted that the <br /> gradients for these two events were higher than normal suggesting that off site production <br /> ' is influencing the aquifer A well receptor survey was completed for the site in January <br /> 2001 and two agricultural wells were identified approximately 1600 feet west of the site <br /> (see Map 1, Table 1 -- Appendix D) If these wells were operated during the months in <br /> ' question, it is possible that the Marci site was within the cone of depression created by <br /> the well pumping The shallow aquifer did not reverse during this period and this may be <br /> due to the-domestic wells to the southeast of the site that may be screened shallower than <br /> the agricultural wells and exert a primary influence on the water table that is easterly <br /> e Diesel range petroleum hydrocarbons were detected in three of the site's eleven <br /> monitoring wells <br /> ' • Well MW-5 contained 7310 Rgll diesel and remains the most severely impacted well <br /> • Gasoline range petroleum hydrocarbons (TPH-G) were not detected in any of the wells <br /> for this event Several wells have had at least one event in which TPH-G was detected <br /> ' 0 Minor BTEX constituents are present at levels ranging in small amount in wells MW-4, <br /> MW-5,MW-6 and MW-7 <br /> ' o Motor oil range petroleum hydrocarbons were not present in any of the groundwater <br /> samples at concentrations above the laboratory reporting limits <br /> • Deep wells MW-104, MW-105 and MW-106 did not contain contaminant concentrations <br /> above the laboratory reporting limits Well MW-105 intermittently contains diesel <br /> contamination <br /> o The groundwater samples were analyzed for 1,2-dichloroethane and 1,2-dibromoethane in <br /> accordance with SJCBHD's April 27, 2004 directive No well contained these <br /> contaminant concentrations above the laboratory reporting limit - 0 5 ug/l It is noted that <br /> the reporting limit for well MW-5 was elevated (50 ug/1) due to matrix interference (see <br /> ' page 8 of the Castle Analytical Laboratory report) <br /> • The lateral extent of the diesel groundwater plume is currently undefined to the south <br /> • The vertical extent of the plume is intermittently defined by MW-104, 105, & 106 <br /> ' • Oxidation-Reduction Potential (ORP) measurements show that several monitoring wells <br /> are within the reaction depleted water caused by biodegradation of the contamination <br /> ' plume All the monitoring wells exhibited low to moderately positive ORP values except <br /> MW-105 The ORP data are included in Table 5 of Appendix A <br /> ' An examination of the contaminant distribution and groundwater flow direction data doesn't <br /> reveal any obvious trends A consistent factor previously noted in the investigation was the <br /> increase in diesel concentrations in well MW-5, see Figure 6- MW-5 TPH-D vs <br /> ' Groundwater Elevation The concentrations had previously demonstrated an increasing trend <br /> until June 2002 when wide fluctuations began The plot in Figure 6 suggests that a <br /> previously direct relationship between groundwater elevation and contaminant concentrations <br /> ' has reversed since June 2002 <br />