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Geological Technics Inc. `..t Page 3 <br /> Additional Pilot Test Work Plan <br /> Project No.770.2 <br /> October 30,2008 <br /> r <br /> points within the boundary of the sand channel area. It is possible the sand layer is <br /> laterally continuous across the site as shown by Figure 4. <br /> • Figure 5: Geologic Cross-Section B - B' illustrates the subsurface from the northwest to <br /> southeast sections of the subject area. The section also displays the predominantly fine <br /> grained soils at the site as in Cross-Section A—A'. <br /> The sand layer identified at a depth of 40 - 45 feet bgs in MW-7 was further defined <br /> during the November 2005 CPT investigation. The CPT investigation revealed that the <br /> r., sand layer appears to be ahannel (?) de-po with a southwest-northeast trend as <br /> depicted in Figures 4 & 6. The sand/gray�i;y,layer is present at depths ranging from as <br /> n , shallow as 38 feet in CPT-5'to as deep as4 feet in MW-1. The layer varies in thickness <br /> 46" from seven feet in CPT-1 to less than two feet in CPT-10, A visual analysis of the <br /> G subject depth soil samples retained in chip boxes at GTI's office affirm that the samples <br /> appear to be from the same unit(s). In a predominantly silty/clayey soil profile this <br /> feature has the potential to be a preferential pathway for contaminant migration. Other <br /> sand units with a thickness of less than a few feet to several inches were identified at the <br /> site but they were not shown to be continuous in lateral extent. <br /> `" • As documented in our April 20, 2006 "Site Conceptual Model (March 2006 Revision)" <br /> veins and/or fractures identified in soil samples appear to be a direct route for the vertical <br /> migration of the diesel. <br /> 2.2 Hydrogeology <br /> There are no surface water bodies near the area of sufficient size or volume to act as a <br /> hydrogeologic boundary. An irrigation ditch/canal is adjacent to the north of the parcel and it <br /> may act as a shallow aquifer recharge source. Regionally, groundwater is utilized as a source <br /> for domestic, agricultural, and industrial supply water. i <br /> The groundwater elevations observed in the water table wells ranged from approximately-28 <br /> to -44 feet mean sea&Wvel (MSL) since August 2000. This corresponds to a depth to <br /> groundwater of 51 - 67 feet below grade surface (bgs). The site's shallow aquifer displays <br /> «r highly variable shifts in groundwater direction. But the groundwater direction has been <br /> predominantly to the southeast since additional wells were installed in May 2002. The <br /> horizontal gradient measurements for the study area range from 0.0001 to 0.017 ft/ft during <br /> the 2000—2008 monitoring period. <br /> The deep well groundwater elevations also ranged from approximately -28 to -44 feet mean <br /> .. sea level (MSL) since August 2000. This corresponds to a depth to groundwater of 51 - 67 <br /> feet below grade surface (bgs). The deeper aquifer flow has been consistently to the east <br /> except for the April 28 and May 23, 2003 events, during which time the gradient reversed <br /> .� 180°from an easterly direction to a westerly direction. This suggests that the regional well <br /> pumping causes significant fluctuations in groundwater direction. The horizontal gradient <br /> measurements for the deeper aquifer level ranged from 0.001 to 0.007 ft/ft during the 2000 — <br /> �' 2008 monitoring period. <br />