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Stanislaus River. Groundwater generally flows toward pumping wells located north and south of <br /> the Stanislaus River. <br /> The alluvial aquifer system underlying the Study Area consists of three high-producing water- <br /> bearing zones designated as the Upper Aquifer, the Intermediate Aquifer, and the Lower <br /> Aquifer. Each of these typically contains more than one water-bearing unit with similar water <br /> level elevations and water chemistry. Aquitards consisting of fine-grained silts and clays <br /> generally separate water-bearing units. Four stratigraphic intervals are as follows: <br /> 1. Upper Aquifer (water table at 20 to 40 feet bgs down to approximately 100 to 115 feet bgs): <br /> The B-zone extends from 20 and 45 ft bgs. The underlying A-zone consists of the Upper A- <br /> zone (approximately 50 to 80 feet bgs), Middle A-zone (approximately 80 to 95 feet bgs) and <br /> Lower A-zone (approximately 100 to 115 feet). <br /> 2. Intermediate Aquifer (Approximately 110 to 190 feet bgs): Monitored by Nestle's C1 wells, <br /> generally constructed with slotted intervals between 130 to 150 ft bgs and C2 monitoring <br /> wells, generally constructed with slotted intervals between 175 to185 feet bgs. <br /> 3. Corcoran Clay (178 to 210 feet bgs): A regionally extensive blue-green lacustrine clay <br /> forms an aquitard (confining unit). <br /> 4. Lower Aquifer (> 210 feet bgs): Nestle's D-level monitoring wells generally screened from <br /> 220 to 240 feet bgs. Water below approximately 700 feet bgs is no longer potables <br /> A1.8 ON-SITE AND OFF-SITE TCE SOURCE AREAS <br /> To date, investigation activities within the Study Area have identified the On-Site source area <br /> (the former manufacturing facility) and two main source areas off site (the City of Ripon WWTP, <br /> and sewer lines leak near 519 Stockton Ave). The investigation activities included reviews of <br /> historical facility operations and waste discharge practices, pumping data from On-Site <br /> production wells, groundwater and soil investigation data, soil vapor surveys, and fate and <br /> transport modeling. The details of these investigations can be found in the Updated SCM <br /> document prepared by AMEC-Geomatrix34 and the 2011 Revised FS Report prepared by <br /> ECMss <br /> A1.9 SITE REMEDIATION <br /> Nestle has completed several remedial activities and tested several remedial technologies <br /> including: <br /> • Soil vapor and soil remediation, <br /> • Source area in situ remediation pilot studies near the extraction wells EI-1 and EW-1 and <br /> monitoring wells M-1A and M-113, including injection of a protein substrate in 198936 <br /> potassium permanganate in 200037, and a carbohydrate substrate (molasses) in 200538, <br /> and <br /> • Groundwater remediation by pump and treat. <br /> Remediation efforts included targeting removal of COC mass in soil and soil vapor as well as <br /> long-term groundwater extraction and treatment in areas of elevated COC concentrations. <br /> Some of these areas have been remediated and the details of associated activities can be <br /> found in previous reports3s,4o,4, Nestle installed a groundwater extraction and treatment system <br /> for well E-2 at the Stockton Avenue (Off-Site) location in 1999. Pumping began at E-6 in 2004. <br /> Combined extracted water from E-2 and E-6 was discharged to the City non-potable water <br /> system (NPS). <br />