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Ms. Kerry Heckman - 2 - 1 June 2006 <br /> 2211 N. Wilson Way, Stockton, San Joaquin County <br /> The depth to water varied from 42.84 to 44.64 feet below the top of the well casings. The <br /> groundwater gradient varied from 0.01feet/feet (ft/ft) to 0.002 ft/ft. The downgradient <br /> groundwater flow direction in HU-1/2 (40-100 ft bgs) and HU-3/4 (100-150 ft bgs) varied in all <br /> directions due to mounding in the SVE extraction wells area, and in an apparent easterly and <br /> southerly direction outside of the influence of the SVE extraction wells. Deeper zone HU-5/6 <br /> (150-250 ft bgs) groundwater flowed in an apparent easterly and southerly direction. <br /> Comments: <br /> 1) Report: The lack of notice to Regional Board staff of SVE/AS treatment system <br /> stoppage and the ensuing 44-day hiatus of the SVE/AS treatment does not comply with <br /> MRP No. R5-2005-0827. The MRP requires notice to Regional Board staff within <br /> 48 hours of shutdown of the remediation system, and provides a schedule for required <br /> sampling and analyses for each quarter. I discussed the issue of notification with AGE <br /> in a meeting on 12 May 2006 and received an emailed letter of explanation (attached) <br /> on 15 May 2006. The email explanation stated that issues with PG&E over dual billing <br /> from two electrical meters for the SVE system and modifications to provide one <br /> electrical meter were the reason for the delay. AGE stated that all future unscheduled <br /> stoppages of the treatment system would be noticed promptly to Regional Board staff <br /> within 48 hours of the stoppage, per MRP No. R5-2005-0827. Note that dual billing of <br /> charges to the State Water Resources Control Board UST Cleanup Fund is prohibited. <br /> %Alk;i,. 4-ke 1AI 1,.,1.,,•, � 4r♦roc L- me-%c+ of+k,= iccl Inc rainfarl to n�nna iniartinn <br /> G� VVLJ1AJ 1C711. V Vl111e U lc VVVII-1r. 1C111 CAUUI lrOOII Iv­' a Iv vv...vv •.. ..••-• ••• ----•-••, <br /> there are some elements missing from the Workplan. In future workplans for ISCO <br /> remediation (including ozone injection) please review and incorporate applicable <br /> guidance from the Interstate Technology & Regulatory Council (a workgroup that is <br /> recognized by the State of California), which may be downloaded from the Internet at <br /> http•//www.itrcweb.org/qd ISCO.asp. <br /> 3) The BST section of the Workplan is approved at this time with the modifications listed <br /> below. <br /> A). Pages 8 and 9 — The iisi of BST analyses are riot complete. Add broi mide and <br /> bromate to the list of general minerals. Analyze all constituents in a manner to provide <br /> a degradation rate if these by-products of ozone injection are detected. Note that <br /> detection limits should be low enough to compare results to the Water Quality <br /> Objectives, which can be downloaded from the website in the header of this letter. <br /> B). Total Organic Carbon (TOC) and Soil Oxidation Demand (SOD) analyses are <br /> necessary components for an ISCO remediation design. Add TOC and SOD to the list <br /> of BST analyses. <br /> C). The BST does not include a separate test to determine whether volatilization <br /> alone (air sparging) would significantly reduce the constituents of concern (COCs) at a <br /> cost savings over ozone injection. Include a BST lab analysis simulating the use of air <br /> sparging alone for petroleum hydrocarbon COCs. <br /> D). Provide an evaluation in the Geochemical Evaluation of any effects noted in the <br /> BST that would degrade water quality or that might affect aquifer characteristics when <br /> scaled up to the OPS. <br /> E). Page 10, the Geochemical Evaluation should be reviewed and signed by a <br /> geochemist or chemist familiar with soil chemistry. <br />