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MONITORING WELL INSTALLATION WORK PLAN <br /> 1.0 INTRODUCTION <br /> In 2001, five groundwater monitoring wells were installed at the Pilkington North America, Inc. <br /> (Pilkington) facility located at 500 East Louise Avenue (Site), Lathrop, San Joaquin County, California <br /> (Figures 1 and 2, Appendix A). The wells were installed under Waste Discharge Requirements (WDR) <br /> Order No. 5-01-114 issued by the Central Valley Regional Water Quality Control Board (Regional <br /> Board) dated May 24, 2001. Subsequent to installation, the wells have been sampled according to <br /> Monitoring and Reporting Program(MRP)No. 5-01-114. <br /> The work plan for the initial monitoring well installation was approved by the Regional Board in a letter <br /> dated August 14, 2001. In that letter, the Regional Board indicated that a measured gradient different <br /> than the assumed gradient to the north may require the installation of additional well(s). Subsequent <br /> monitoring has indicated a general gradient to the south. Consequently, in a letter dated January 18, <br /> 2005, the Regional Board directed the installation of additional groundwater monitoring wells. <br /> This work plan was prepared by Condor Earth Technologies, Inc. (Condor) at the request of Pilkington to <br /> propose the location of two additional monitoring wells constructed identically to the existing wells. <br /> 2.0 SITE BACKGROUND INFORMATION <br /> Pilkington operates a float glass furnace facility at the Site. The facility stockpiles raw material, <br /> manufactures glass products, and warehouses products prior to shipment. Wastewater is generated from <br /> groundwater infiltration, float glass manufacturing, cooling tower and boiler blowdown,reverse osmosis <br /> reject water, and domestic wastewater. Domestic wastewater is disinfected prior to commingling with the <br /> process water. The area within the Site boundaries consists of approximately 176 acres. Approximately <br /> 75.4 acres are available for land application of wastewater. Wastewater has been applied to the lawn <br /> areas (11.4 acres), Site A (42 acres), and Site C (8.5 acres). Approval for the use of Site B has been <br /> requested of the Regional Board. The Site layout is shown on the map (Figure 2). The potential impact <br /> I of water storage and discharge to land is regulated by the WDR cited above. <br /> 3.0 MONITORING WELL LOCATIONS AND RATIONALE <br /> Two additional monitoring wells are proposed for the Site. The locations and rationale for each <br /> "- monitoring well are described in this section. The proposed monitoring wells are shown on Figure 2. <br /> The first proposed additional monitoring well will be located at the west end of the facility, and at the <br /> southern end of the lawn area. This location is expected to provide the most southerly location of the <br /> irrigated lawn areas. The second proposed monitoring well will be located near the southern end of Area <br /> B. This location is intended to provide down-gradient monitoring for both Areas B and C. <br /> As has been previously noted, the below-grade facilities in the area of the furnace are below existing <br /> groundwater, and sump pumps discharge infiltrating water out of these basements. Consequently, there <br /> is a localized gradient in the immediate area of the eastern half of the facility. The two additional <br /> monitoring wells are at a sufficient distance from these basement sumps that they are expected to indicate <br /> the area gradient and not the localized gradient produced by the dewatering sumps. <br /> IL 1) CONDOR <br />