Laserfiche WebLink
' QologwaI7echa=t u Page 6 <br /> Groundwater Monitoring Report <br /> Project No 770 2 <br /> February 7,2005 <br /> ' plume All the monitoring wells exhibited low to moderately positive ORP values except <br /> MW-4 and MW-105 The ORP data are included in Table 5 of Appendix A <br /> • The lateral extent of the diesel groundwater plume is not fully defined by the outer ring of <br /> wells (MW-3, 6 & 8), but the concentration of diesel is very low in these wells <br /> • The vertical extent of the plume is intermittently defined by MW-104, 105, & 106 The <br /> t groundwater around MW-105 is contaminated, however concentrations are so low that <br /> further investigation may not be needed at this time <br /> MW-5 <br /> An examination of the contaminant distribution and groundwater flow direction data reveals <br /> groundwater elevation is slowly declining since 2000 and that diesel concentrations are <br /> overall fairly stable, except for the August 2004 monitoring event A consistent factor <br /> previously noted in the investigation was the fluctuation in diesel concentrations in well <br /> MW-5 (see Figure 6- MW-5 TPH-D vs Groundwater Elevation) The concentrations had <br /> ' previously demonstrated a slight increasing trend until June 2002 when concentrations began <br /> to fluctuate for about a year Subsequently, the concentrations have been very consistent, <br /> except for August 2004 The cause for the very high spike in August is unclear, possibly due <br /> to low water level in the well and associated poor recharge to the well during purging and <br /> sampling Purging and sampling logs suggest that sample quality may be compromised due <br /> to low water level in the well The plot in Figure 6 suggests that a previously direct <br /> relationship between groundwater elevation and contaminant concentrations has reversed <br /> since June 2002 <br /> 1 Well MW-5 continues to contain the highest concentrations of detected contaminants (see <br /> Figure 8) it is not down gradient of the former UST location and the reason for this anomaly <br /> is not known, but could be related to geologic units that slope to the west <br /> ' MW-4 <br /> Well MW-4 lies adjacent to the former UST field Figure 7-MW-4 TPH-D vs Groundwater <br /> ' Elevation suggests that a predominantly inverse relationship exists between groundwater <br /> elevation and contaminant concentrations In this figure the sudden increase in diesel <br /> ' concentrations for August 2004 coincides with the same phenomenon observed in MW-5 <br /> The cause is unknown at this time, but the concentration of diesel has decreased since that <br /> event <br /> ' MW-105 <br /> TPH-D was detected in MW-105 at 94 ug/l Detection of TPH-D in the last two quarters <br /> ' indicates that the contamination is moving vertically downward in an oblique angle to the <br /> northwest from the source <br /> ' In Figure 9— MW-5 & MW-105 TPH-D versus Groundwater Elevation, well MW-5 <br /> contaminant concentrations have previously exhibited a weak correlation with changes in the <br /> water table Since September 2001 the relationship has been reverse Well MW-105, <br />