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Mr. Mike Desso • - 4 - • 15 September 2008 <br /> Nestle USA Inc. <br /> Other Comments <br /> The comments listed below address the following items: <br /> 5. California Department of Transportation (Caltrans) impacted irrigation well, <br /> 6. Migration of COCs northwest of the Former Facility, <br /> 7. Figure 2 well location map, <br /> 8. Groundwater flow and transport model, <br /> 9. Several text reference items, and <br /> 10. Reference corrections. <br /> 5. Caltrans well. Section 2.1, Item 7 summarizes Nestle's efforts to provide replacement <br /> water to the California Department of Transportation (Caltrans) for the impacted <br /> irrigation well on Manley Road in Ripon. Caltrans has denied Nestle access to replace <br /> the well with hookup to the City of Ripon (City) non-potable water system. <br /> Concentrations of COCs continue to decline in the well: concentration TCE has steadily <br /> dropped from a high of 6.3 micrograms per liter (µg/L) in April 2000 to a low of 0.75 4g/L <br /> in October 2007; concentrations of cis-1,2-DCE have dropped from a high of 190 µg/L in <br /> May 2002 to a low of 1.1 µg/L in April 2007. If Caltrans will not allow access, the <br /> Regional Water Board will not require Nestle to provide replacement water. <br /> 6. Northwest migration of COCs. The Annual Report cites conditions at City municipal well <br /> MW-10 as a measure of the effectiveness of the two operating Nestle groundwater <br /> treatment systems: "Municipal well MW-10 has not exhibited COCl above detection' <br /> limits over the course of the last 7 years of sampling from this well." However, it must be <br /> noted that in 2006 (after 5 years of sampling) breakdown products of TCE appeared and <br /> continue to be present in 2 water supply wells at Ripon Elementary School and Ripon <br /> Christian School. Although concentrations have not exceeded Public Health Goals <br /> published by the State of California and do not appear to be increasing rapidly, these <br /> school wells are located in the groundwater flow path between the Former Facility and <br /> MW-10. They are approximately 2,500 to 3,500 feet down-gradient of the Former Facility <br /> and 1,600 to 2,500 feet up-gradient of MW-10. <br /> 7. Well location map. Figure 2 should include a grid with lines drawn at intervals of <br /> approximately 1,000 feet and grid labels along the map margins. The font size used to <br /> depict the well names on the map should be significantly reduced (similar to the font of <br /> the vapor extraction [VE] wells at Industrial Avenue shown on the map). A well location <br /> key that references the location of each well using north-south and east-west grid <br /> coordinates should be added to the map. There appears to be sufficient space in thq <br /> upper right corner of the map to place such a key. The grid map should be included in <br /> future annual reports. <br /> 8. Groundwater model. The Annual Report's Section 1.10, presents assessment of the <br /> capabilities of the groundwater flow and contaminant transport model developed by <br /> ECM. Statements are made regarding plume migration based on model simulations. <br /> However, remedial action decisions should be made based on actual plume constituents <br /> of concern (COC) concentration data. <br />