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Joe Lentini - 2 - 5 November 2010 <br /> Shell Mountain House <br /> groundwater ranged from about 28 to 35 feet bgs. Groundwater flow generally was toward the <br /> northwest in Neighborhood B and to the northeast in Neighborhoods C and D. Gradients <br /> ranged from 0.002 to 0.02. Groundwater samples were submitted for laboratory analysis of <br /> total petroleum hydrocarbons as diesel (TPHd), TPH as crude (TPHc), BTEX, and <br /> naphthalene. Consistent with results observed in previous quarters, no TPHc, TPHd, BTEX or <br /> naphthalene was detected in any of the groundwater samples obtained from Neighborhoods <br /> B, C or D. Overall, the third quarter groundwater monitoring results were consistent with <br /> results observed in previous quarters. <br /> Our comments are presented below. <br /> 1. The analytical laboratory testing that detected the helium tracer gas at 28,200 pg/m3 <br /> (28.2 pg/L) was performed at a detection limit (DL) that greatly exceeded the DTSC's <br /> suggested DL of 10 pg/L' for this compound. Although the presence of the leak potentially <br /> presents some doubt as to whether BTEX in SVP-1 is actually non-detect (ND), resampling <br /> is not warranted. The results of soil vapor sampling conducted in December 2006 in the <br /> area of SPV-1 and in other excavation areas detected benzene in soil gas as high as <br /> 570 pg/m3. Johnson & Ettinger (J&E) modeling of the highest benzene concentrations in <br /> these areas showed that the soil gas posed no incremental cancer risk from intrusion into <br /> indoor air in excess of the one-in-a-million de minimis standard. The totality of the results <br /> indicate that the residual concentrations of petroleum hydrocarbon contamination in soil <br /> gas in Area 5 warrant no further action (NFA). <br /> 2. With the exception of a few detections of TPHd that were below the water quality objective <br /> of 100 pg/L, the monitoring results over the past five quarters have been ND for petroleum <br /> hydrocarbons. These results indicate that it is appropriate for Shell to request an NFA <br /> determination for this Site. As discussed in previous correspondence, Shell anticipated that <br /> it would submit an NFA request. Please submit the request by 10 January 2011. Staff will <br /> review that report to determine if NFA is appropriate and make recommendations for <br /> attaining site closure. <br /> 3. A review of the State Water Resource Control Board's (State Water Board's) GeoTracker <br /> database indicates that electronic data deliverables (EDFs) from 2008, 2009 and before <br /> 2007 have not been submitted. The x, y, z well survey data are also absent. The <br /> GeoTracker Global Identification number for this site is SL06077772408. Be advised that <br /> submission of site data to the GeoTracker database was required starting in September <br /> 2001. Submission to the State Water Board's GeoTracker database is required by Title 23 <br /> and Title 27 the California Code of Regulations. All documents, including work plans, <br /> correspondence, quarterly monitoring reports, investigation/cleanup reports, etc., and all <br /> analytical and site data must be electronically uploaded to the GeoTracker database and is <br /> due at the time the paper copy is submitted to this office. Until you receive further direction <br /> from Central Valley Water Board staff, you will be required to submit paper copies of all <br /> reports and correspondence. For specific information about EDF submittals, you may call <br /> the GeoTracker help-desk at (916) 327-3918 or log on to the State Water Board's <br /> GeoTracker web site at: http://www.geotracker.swrcb.ca.gov, and click on the Electronic <br /> Advisory—Active Soil Gas Investigations, Department of Toxic Substances Control/California Regional Water <br /> Quality Control Board Los Angeles Region, 28 January 2003 <br />