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Groundwater Well Installation Work Plan Sharpe Army Depot <br /> Lathrop, California <br /> Sharpe was placed on the National Priorities List in 1987 and entered into a four-party agreement in 1989. <br /> As described in the FFA,the authority for environmental restoration decision-making rests with a team of <br /> remedial project managers from the following four parties: <br /> • California Department of Toxic Substances Control <br /> • Central Valley Regional Water Quality Control Board <br /> • U.S. Environmental Protection Agency, Region 9 <br /> • Sharpe Army Depot <br /> The DLA transitioned Sharpe back to the U.S. Department of the Army (Army) effective October 1, 2014. <br /> The Army is the lead agency responsible for funding and implementing remedial actions at Sharpe. <br /> The FFA established two OUs to facilitate environmental restoration at Sharpe. OU 1 addresses <br /> groundwater in four saturated monitoring zones (designated as A, B, C, and D) contaminated primarily <br /> with volatile organic compounds (VOCs). The OU 1 Record of Decision (ROD; ESE, 1993) documents <br /> groundwater extraction, treatment, and discharge of treated effluent as the selected remedy for <br /> contaminated groundwater. The Explanation of Significant Differences for OU 1 (URS, 2014) was signed <br /> and approved by the regulatory agencies and the Army in September 2014 and adds in situ treatment of <br /> high levels of subsurface contamination and land use controls to the remedy. OU 2 addresses soil and soil <br /> gas above the water table. The OU 2 Record of Decision (ROD; ESE, 1996) documents the extraction and <br /> treatment of VOC-contaminated soil vapor"no further action" decision at multiple sites. In June 2011,the <br /> Amendment to the OU 2 ROD (URS, 2011) modified the No Further Action decision to ensure <br /> protectiveness by adding land use controls at ten sites and biological monitoring at two sites for the <br /> burrowing owl (Athene cunicularia), a California Species of Special Concern. <br /> 1.2 Geology and Hydrogeology <br /> The Sharpe area contains one complex, heterogeneous aquifer system, in which four hydrostratigraphic <br /> zones are located between 14 and 270 feet (ft) below ground surface (bgs). These hydrostratigraphic <br /> zones are considered distinct zones to monitor hydraulic gradients and contaminant migration.The zones <br /> include several saturated transmissive layers (sands) 5 to 12 ft thick in the following depth intervals: <br /> • A Zonewater table to 40 ft bgs <br /> • B Zone40 to 90 ft bgs <br /> • C Zone90 to 170 ft bgs <br /> • D Zone170 to approximately 280 ft bgs <br /> In the A Zone, groundwater is generally unconfined; however, the fine-grained deposits in the Lower A <br /> Zone and Upper B Zone (also known as the A/B aquitard) locally create confining conditions. Although <br /> there is good continuity of the confining layer across Sharpe, groundwater and dissolved contaminants <br /> can move from the A Zone through the B Zone and into the C Zone.This movement can occur because the <br /> confining layer in some areas is thinner and contains more sand. Pumping onsite and offsite water supply <br /> wells has caused strong vertical hydraulic gradients. The B, C, and D Zones have hydraulic characteristics <br /> of leaky confined aquifers. <br /> Subsurface soils vary from clay and silt to coarse sand. Within each zone, deposits containing each soil <br /> type occur; however,the deposits vary in thickness vertically and horizontally across Sharpe. Silt and clay <br /> Ahtna Environmental,Inc. 3 <br />