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Mr. Carl W. Knowles, Successor Trustee Page 4 of 5 <br /> Knowles Family Trust 23 December 2009 <br /> Former Roek Construction <br /> 102 S. Wilson Way <br /> As the discussion of contaminant concentration trends in the subsurface was not presented in <br /> the RCC by a properly licensed professional, the EHD will not comment on it in detail at this <br /> time; however, it should be noted that the EHD has concurred with GZA's interpretation that <br /> dissolved MTBE on your site is the result of on-site migration from unauthorized UST system <br /> releases on either the former Top Filling site or the Arco site, and by letter dated 23 February <br /> 2009, the EHD relieved you of any further sampling responsibility for monitoring wells MW-3, <br /> MW-4, MW-7, MW-14, MW-16A and MW-16B. The EHD has left some wells that contain MTBE <br /> on your sampling regimen because the EHD interprets other contaminants, for example 1,2- <br /> DCA, to be from your release. If it can be convincingly demonstrated to the EHD that any wells <br /> you still sample are predominantly impacted by one of the off-site releases, and that the <br /> information derived from such wells does not contribute to the proper management or <br /> characterization of your plume, the EHD will also remove them from your sampling regimen. <br /> To be clear, the EHD does not expect you to remediate the migrating MTBE plume or <br /> trespassing TPHg and BTEX from one of the off-site releases; in fact the EHD specifically noted <br /> in the directive by letter dated 31 August 2005, that MTBE was not a target contaminant of the <br /> directive to submit a work plan for interim groundwater remediation. Your directives are to <br /> address groundwater impacted by your unauthorized release, which is typically characterized by <br /> the presence of TPHg, BTEX, 1,2-DCA, and on occasion, locally by ethylene dibromide (EDB). <br /> Over a 2-year period, from November 1997 to December 1999, a soil vapor extraction unit <br /> operated on your site, removing an estimated 12,700 pounds of contaminants. GZA estimates <br /> that an additional 750 pounds of hydrocarbons resides in soil above the groundwater and <br /> 15,000 pounds resides in soil saturated by groundwater. The residual 22,500 pounds of <br /> contaminants is apparently the source of contaminants that continually flux into groundwater, <br /> maintaining the plume of groundwater impacted by TPHg, BTEX and 1,2-DCA. No active <br /> remediation has occurred at the site for the last 10 years despite efforts by the EHD to address <br /> the impacted groundwater issue; such efforts go back as far as 20 July 2001 when the EHD <br /> recommended by letter that the feasibility of in situ air sparging and groundwater extraction <br /> should be evaluated and directed by letter dated 04 January 2002 evaluation of ozone injection. <br /> More recently the EHD directed by letters dated 31 August 2005 submission of a work plan for <br /> interim groundwater remediation, 26 October 2006 preparation of a corrective action plan or <br /> feasibility study, and 23 February 2009 submission of a corrective action plan and reinitiate soil <br /> vapor extraction; none of these directives have been met to date; the due dates have been <br /> ignored. GZA recommended in a report dated 06 October 2005 repair and reinitiating operation <br /> of the soil vapor extraction unit on your site, which the EHD approved by letter dated 26 October <br /> 2006, but the approved scope of work has not been implemented. The EHD does not <br /> understand why the unit could not be repaired and returned to operation over the three-year <br /> period that has elapsed since the EHD approved the GZA recommendation. <br /> Finally, the EHD cannot comment in detail on the applicability of the Chevron case that resulted <br /> in the State of California State Water Resources Control Board Order WQO 2004-0005, as the <br /> applicability of that case was not presented by a properly licensed profession showing how the <br /> site-specific details of the Chevron case are closely matched by your site characteristics. The <br /> Chevron case circumstances in the Order are given in general terms, and the details of the two <br /> sites' hydrogeology, contaminant species, concentrations and masses are not provided that <br /> would enable the EHD to evaluate the applicability of WOO 2005-0005 to your site. If you wish <br /> further consideration of this issue, have your consultant submit a report that supports your <br /> argument. You should be aware that the EHD believes that your site data overwhelmingly <br /> Site Closure Request Response 1209 <br />