Laserfiche WebLink
j <br /> C,eologlut7_ec"iesW Page 2 <br /> Groundwater Monitoring Report <br /> Project No.750.2 <br /> i August 16,2002 <br /> 1 <br /> i <br /> The internal=combustion engine (I.C.) was set ij n operation on February 5, 2002. The IC ran <br /> until February 27, 2002 when it was shutdown and removed from the site because it was not <br /> j 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. <br /> f ri <br /> 1.0 GROUNDWATER MONITORING <br />{ u <br /> 1.1; Hydrogeology of Site i <br />� L <br /> The dominant soil type in the upper 75 feet of subsurface geologic soils investigated is sand <br /> r 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 June 28, 2002, event was about 55.47 feet above <br /> i mean sea level, which is consistent with previously measured average elevations at the site. <br />{ The groundwater elevation represents an decrease of approximately 0.48 feet since the <br /> monitoring event of March 14, 2002. <br /> Groundwater gradients were calculated for theJune 2002 event. Groundwater was flowing <br /> N68°W at 0.0019 ft/ft. MW-1, MW-2 and MW-3 were used for the gradient calculations. <br /> l The elevation, gradient and bearing data are summarized in Table 1, Appendix A. The <br /> gradient direction is illustrated on Figure 2: Gradient Map. Historical groundwater , <br /> k directions and gradients are presented in Figure 3: Groundwater Gradient Rose Diagram. <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 /> i <br />