Laserfiche WebLink
3.2 Fate and Transport Analysis <br /> �r <br /> 3.2.1 Geology <br /> �. The U.S.D.A. Soil Conservation Service maps the on-site soils as Stockton Clay, which is a <br /> fine-textured, dark gray to black clay, deposited by quiescent or slow moving water. The <br /> parent material was of mixed origin, but primarily igneous rock. The U.S. Geological Service <br /> ~ maps the deeper site geology as "basin deposits", dominated by fine-textured earth materials, <br /> and intercalating layers of coarser textured materials, capable of releasing groundwater. <br /> Based on site investigation results, the soils observed to the total drilling depth of <br /> approximately 160 feet, consisted of massive intervals of clay and silt mixtures, interrupted by <br /> �. relatively thin intervals of sandy soils. As shown on the stratigraphic cross-section (Figure <br /> �.. 12), sandy soil intervals appear to become more massive and laterally continuous with depth. <br /> The sand interval between 110 and 125 feet bgs was observed in all six CPT borings at a <br /> thickness of up to 10 feet. The sands observed within this interval were the thickest, most <br /> �... laterally continuous, and present over the greatest aerial extent. Sands were also observed <br /> between 140 and 160 feet bgs in.ail six CPT borings; However, these sands appeared <br /> interbedded and less massive than the sands in the 110 to 125 foot interval. All of the soil <br /> v boring, monitoring well and CPT logs for the project are included in Appendix C. <br /> 3.2.2 Hydrogeolo-gy <br /> �. Between August 1990 and May 1992, during the installation of MW-1, MW-2 and MW-3, <br /> saturated soil was first observed at a depth of between 68 and 70 feet bgs, and the static <br /> depth to groundwater ranged from 65 to 67 feet bgs. In May 1994, during the installation of <br /> MW-4 and MW-5, saturated soil and static groundwater were first observed at a depth of <br /> approximately 60 feet bgs. This suggests that groundwater beneath the site was present <br /> under water table conditions, and that the groundwater elevation was on the rise. By January <br /> 1996, the continued rise in the groundwater table resulted in the static groundwater elevation <br /> ' above the tops of the screened intervals in all five original groundwater monitoring wells. <br /> To re-establish a groundwater table monitoring and sampling capability at the site, Ramage <br /> Environmental supervised the installation of MW-6 and MW-7 in April 1998, and began <br /> .. monitoring and sampling these Wells and the two deep soil vapor extraction wells (VW-1 D <br /> and VW-2D). Saturated soil and groundwater were first encountered during the installation of <br /> MW-6 and MW-7 at a depth of approximately 43 to 44 feet bgs. Between May 1998 and <br /> December 2005, the static depth to groundwater beneath the site has stabilized from <br /> between approximately 35 to 50 feet bgs. Between May 1992 and December 2005, the <br /> groundwater table elevation rose approximately 23 feet. <br /> 14 <br />