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Weston Solutions, Inc. <br /> Remedial Action Work Plan for the San Joaquin County Human Services Agency Site—Stockton, California <br /> GEOLOGY AND HYDROGEOLOGY <br /> cross-section (shown on Figure 3-1). Analytical results from recently collected groundwater <br /> samples are also shown on the cross section. <br /> Groundwater elevations have historically ranged from approximately 20 feet bgs in 2020 to 50 <br /> feet in 1991. The original wells (MW-1 though MW-3) were installed in December 1988; <br /> however, the water table dropped 15 feet shortly thereafter, and deeper wells (MW-4 through <br /> MW-8) were installed in August 1991 as well as replacement monitoring wells (MW-2A and <br /> MW-3A) in 1995. The water table has rebounded 25 feet since 1991, with a small decline <br /> between 2001 and 2006. Seasonal fluctuations in groundwater elevations of less than 2 feet are <br /> apparent. <br /> The groundwater flow direction—calculated using water level data from MW-3A, MW-6 and <br /> MW-9—has historically flowed east to northeast at a gradient ranging from 0.0015 to 0.004 <br /> feet/foot. The groundwater flow direction during the recent period of high potentiometric <br /> surface elevations has been northeast. A groundwater elevation contour map from the 4th <br /> quarter 2020 monitoring event is shown on Figure 3-2. <br /> A tidal study was conducted on well MW-4 on 9 November 1991 where a 0.10-foot decrease <br /> in elevation was observed between high tide and low tide over a 4.5-hour period. The tidal <br /> change recorded at the port of Stockton was a decrease of 1.7 feet. A buried stream channel <br /> leading from McLeod Lake, located 0.33 mile northwest of MW-4, is likely the tidal hydraulic <br /> conduit. A historical map of Stockton from 1849 was reviewed and shows a former slough <br /> connecting McLeod Lake to Mormon Slough running through the HSA property. Tidal <br /> variations are not believed to have any measurable impact on contaminant transport at the Site. <br /> The hydraulic conductivity of the shallow groundwater zone was estimated by conducting slug <br /> tests in wells MW-4, MW-6, and MW-8 in October 1991. The rising head data were analyzed <br /> using Aqtesolv software to determine the hydraulic conductivity. Wells MW-4 and MW-6 had <br /> similar hydraulic conductivity of 0.00 15 foot/minute for the silt aquifer material. Well MW-8 <br /> had a slightly greater hydraulic conductivity of 0.002 foot/minute for the silt and sand aquifer <br /> material. <br /> 3-2 February 2021 <br />