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GeologicalTecklicslnc. Page 2 <br /> Groundwater Monitoring Report <br /> Project No.750.2 <br /> December 10,2002 <br /> properly controlling emissions. The IC was completely rebuilt and returned to the site on <br /> April 22, 2002 and restarted. The IC operated until late May when it was again removed <br /> from the site due to mechanical failure. The IC was rebuilt again and returned to the site on <br /> June 14. The IC has run continuously since June 14 without problems. To date the VETS <br /> has removed approximately 650 gallons of gasoline from the subsurface. <br /> 1.0 GROUNDWATER MONITORING <br /> 1.1 Hydrogeology of Site <br /> The dominant soil type in the upper 75 feet of subsurface geologic soils investigated is sand <br /> with fine to coarse-grained texture. Varying amounts of silt, silty sand and laterally <br /> discontinuous clay lenses were encountered from borehole to borehole. A thick clay layer <br /> was encountered starting at 95-feet in SB-101/MW-101 and continues to at least 115-feet. <br /> The average groundwater elevation on the September 23, 2002, event was about 56.16 feet <br /> above mean sea level, which is consistent with previously measured average elevations at <br /> the site. The groundwater elevation represents a decrease of approximately 1.5 feet since the <br /> monitoring event of March 14, 2002. <br /> Groundwater gradients,were calculated for the June 2002 event. Groundwater was flowing <br /> N830W at 0.0013 ft/ft. The gradient was calculated from the groundwater contours that <br /> were generated using the contouring program, Surfer 7. The elevation, gradient and bearing <br /> data are summarized in Table 1, Appendix A. The gradient direction is illustrated on Figure <br /> 2: Gradient Map. Historical groundwater directions and gradients are presented in Figure 3: <br /> r <br /> Groundwater Gradient Rose Diagram, which shows a consistent westerly flow direction. <br /> Vertical Groundwater Gradients <br /> Under vertical groundwater flow conditions, the water level in a monitoring well is a <br /> function of the length of the well screen and its depth or vertical position in the aquifer. As <br /> with horizontal flow conditions, the diameter of the well or piezometer is immaterial. <br /> The following procedure is used to calculate vertical groundwater gradient: <br /> • Determine vertical distance between the two measuring devices by the distance from the <br /> mid-point between the top and bottom seal of the deep well (MW-101) and the mid- <br /> point between the groundwater elevation and the bottom seal in the shallow well (MW- <br /> 1). <br /> • Measure the head in both wells used in the calculations. <br /> • If the lateral distance between the well pair is greater than a few feet, then calculations <br /> must be made to correct the down-gradient piezometric head to account for the sloping <br />