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C7ealogual recluucsInc Page 5 <br /> Groundwater Monitoring Report <br /> Project No 770 2 <br /> April 30, 2003 <br />' As required under AB2886� the laboratory data was submitted electronically to GeoTracker <br /> q <br /> 1 on January 10, 2002 - confinnation numbers 3917768657 & 8680761396 <br />' 20 FINDINGS AND DISCUSSION <br /> The results of the groundwater sample analysis indicate the following <br /> • Diesel range petroleum hydrocarbons were detected in six of the site's eleven <br /> monitoring wells <br /> • Well MW-5 contained 12,300 gg/l diesel and remains the most highly impacted well <br /> I • Gasoline range petroleum hydrocarbons (TPH-G) are present in MW-6 at 67 9 ug/l <br /> This is the second time that TPH-G was detected for this well for the ten monitoring <br /> events that it has been sampled Four of the wells contained TPH-G for the September <br /> i2001 event only MW-1, 4, 6, & 105 <br /> • Minor BTEX constituents are present at levels ranging from 0 4 --3 7 µg/l in wells MW- <br /> 4, MW-5, MW-6, MW-7 and MW-104 <br /> • Motor oil range petroleum hydrocaibons were not present in any of the groundwater <br /> samples at concentrations above the laboratory reporting limits <br /> • Deep well MW-104 contained 04 ug/l xylene This is the first time the well has <br /> contained detectable contaminants <br /> • Deep well MW-105 contained 84 9 ug/l TPH-D The well has intermittently contained <br />' TPH-D <br /> • Deep well 106 did not contain contaminant concentrations above the laboratory <br /> reporting limits for the third consecutive event <br /> • The lateral extent of the diesel groundwater plume is currently undefined due to the <br /> continuing fluctuations in groundwater direction <br /> • The vertical extent of the plume is intermittently defined by MW-104, 105, & 106 <br /> 0 Oxidation-Reduction Potential (ORP) measurements show that five monitoring wells are <br /> within the reaction depleted water caused by biodegradation of the contamination <br />' plume These wells exhibit negative ORP values and all of the well ORP data are <br /> included in Table 5 of Appendix A The other wells have relatively low positive values <br /> suggesting that the water around these wells are on the outer fringe of the impacted halo <br /> An examination of the contaminant distribution andg roundwater 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 5- MW-5 TPH-D vs <br /> Groundwater Elevation The concentrations had previously demonstrated an increasing <br />' trend, but wide fluctuations are noted for the past four events The plot in Figure 5 suggests <br /> a predominant direct relationship between groundwater elevation and contaminant <br /> concentrations <br />