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Ms. Julie Raming - 2 - 26 April 2000 <br /> "v <br /> B&C performed a pilot scale test of the proposed system in July 1998 which is documented in the <br /> 11 September 1998 Groundwater Extraction/Aeration Pilot Test report. The pilot test data showed that <br /> volatization and impoundment of the spray effluent was successful at reducing chloroform to non- <br /> detectable concentrations. The 36-hour pilot test also showed that the basin infiltration rate was less <br /> than the extraction rate, and B&C did not observe groundwater mounding. However, it is not known <br /> whether hydraulic connectivity was established between the basin and groundwater or whether steady <br /> state conditions were reached. <br /> B&C incorporated the pilot test parameters into the DIRP, which anticipates that approximately 83% of <br /> the extracted groundwater will be discharged to the irrigation canal, and approximately 17%will be <br /> returned to groundwater through the infiltration basin. Since the groundwater extraction rate will exceed <br /> the recharge rate, B&C does not expect groundwater mounding to occur. <br /> I agree with the conceptual plan for the remediation system. The monitoring data consistently show that <br /> the highest concentrations of halocarbons are beneath the stormwater basin (former evaporation pond), <br /> which the DIRP identifies as the objective of the remediation plan The chloroform plume has extended <br /> off-site beneath the housing development to the north which is beyond the anticipated radius of influence <br /> of the extraction wells. Even so, some benefit may be provided by the hydraulic control exerted by the <br /> extraction wells. The DIRP proposes to run the remediation system for three years, evaluate the system <br /> and the off-site plume, and address the off-site portion at that time. <br /> B&C claims that the off-site plume is stable. Although concentrations declined in residential area <br /> monitoring wells BC-12, BC-15, BC-16 and BC-17 since 1985, an increasing trend is evident in BC-13 <br /> and BC-14 between 1985 and 1998. Since 1998, chloroform concentrations have been variable in <br /> BC-13, and decreasing in BC-14. The last three monitoring events suggest that chloroform <br /> concentrations are stable in wells BC-12, BC-15, BC-16, and BC-20 at 48 ug/1, 5 ug/l, 2.7 ug/l, and 2.5 <br /> ug/l, respectively. Monitoring wells BC-12 and BC-13 show the highest of the off-site chloroform <br /> concentrations and are nearest the source area. <br /> Evaluation of the off-site plume should not be delayed for three more years. However, I concur that the <br /> data show that the plume size is not changing appreciably, and the remediation system may exert <br /> hydraulic control limiting plume movement. Therefore, I believe that the off-site plume should be <br /> evaluated after two years of source area remediation. <br /> The DIRP proposes to prepare plans and specifications for the remediation system within 90 days of <br /> Board staff approval. However, the plan is labeled a draft, and I cannot approve a draft document. The <br /> following additional details need to be addressed, as I discussed with Mr. Todd Miller and Mr. Brad <br /> Dickson of B&C during our 18 April telephone conversation. <br /> 1. The stormwater basin also serves water quality functions for the City of Tracy. B&C needs to <br /> provide an analysis of the volume of storage that the City needs to have available in the basin, <br /> when it is needed, the required detention time, and a discussion of how the stormwater needs will <br /> be met concurrently with the remediation system. Although the DIRP states that the conditions of <br /> basin operation will be contained in an Access Agreement between GP and the City, these <br /> elements need to be stated explicity in the remediation plan as well. <br />