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Jerry Moore <br /> 5491 F Street, Banta, California <br /> Page 2 of 3 <br /> • A shift of groundwater flow direction does not mean that a plume formerly pushed <br /> toward the northeast would now be oriented toward the north — plume delineation <br /> toward the northeast is still a necessity. <br /> • The railroad company's requirement for a performance bond and the requirement <br /> for an insurance policy, given the nature of railroad operations and property, <br /> does not seem unreasonable. As these are necessary costs to install the <br /> approved well, the costs may be reimbursable by the State Water Board Cleanup <br /> Fund, although you should check with the Fund to be sure. The EHD will not <br /> waive installation of MW-15 based on this particular cost issue. <br /> • The AEI letter of 10 August 2005 and the railroad company's submittal of the <br /> requirements for an insurance policy and a performance bond to you indicates to <br /> the EHD that the railroad company is being cooperative with you and it appears <br /> that you mainly need to satisfy these requirements to obtain an access <br /> agreement to install and monitor MW-15. <br /> • A technical demonstration has not been presented to the EHD that the purposes <br /> for which installation of MW-15 was approved have been adequately met with <br /> existing wells and data. <br /> If you can provide a technical demonstration that the intended monitoring objectives of <br /> MW-15 are being met with current data, submit a report to the EHD by 15 May 2007 with <br /> the demonstration and the EHD will reconsider the matter, otherwise proceed with <br /> completing the arrangements with the railroad company and install MW-15. Include.in <br /> future quarterly reports updates on the status of your efforts to obtain the access <br /> agreement with the railroad company; note all actions taken by you to reach such <br /> agreement and all responses made by the railroad company during the reported quarter. <br /> The recent sensitive receptor survey findings should be incorporated into a site <br /> conceptual model (SCM) to demonstrate adequate protection of all sensitive receptors <br /> identified in the SRSR. The EHD described the components and uses of an SCM in the <br /> EHD letter dated 30 December 2003. To date the EHD has not received an SCM for <br /> your site. You are directed to prepare and submit an SCM to the EHD by 02 July 2007. <br /> The SCM should include maps and cross-sections that show that the potential receptors <br /> most likely to be impacted by your dissolved plume are adequately monitored through <br /> sentinel wells and/or direct domestic well sampling. <br /> The site investigation report provided the results from two cone penetration test borings <br /> (CPTs) advanced in November 2005. The two borings encountered predominantly <br /> coarse-grained soil (sand and gravel with some silt) from approximately 25 feet below <br /> surface grade (bsg) to total depth of 80 feet bsg, the upper 25 feet of the borings are <br /> characterized by finer-grained soil such as clayey silt, silty clay, silt, and silty sand. Most <br /> of the current groundwater monitoring wells bottom at 20 to 25 feet bsg in the finer- <br /> grained interval; only RW-2 appears to penetrate the uppermost portion of the coarser <br /> soil, bottoming at 30 feet bsg. <br /> The grab water samples collected from CPT1 between 30 and 58 feet bsg did not <br /> contain detectable concentrations of the analytes of concern, but the 78-foot sample <br /> contained 49 milligrams per liter (mg/1) chemical(s) quantified as motor oil (TPH-mo). All <br /> four water samples collected from CPT2 between 28 and 78 feet bsg were impacted by <br />