Laserfiche WebLink
Mr. Jeff Johnson 0 - 2 - 13 October 2010 <br /> Mountain House Site#4 <br /> anticipates beginning the work within 30 days following acceptance of this work plan <br /> and submitting the report by January 2411. <br /> Our comments are presented below: <br /> 1. We are concerned that the proposed sampling plan may not present the most <br /> efficient strategy for achieving the objective of this investigation, which is to delineate <br /> the lateral extent of contamination in soil and vertical extent in groundwater. The <br /> Work Plan does not identify a reliable method for screening soil encountered in the <br /> boreholes for the presence of petroleum, or for collecting discrete samples to <br /> determine the maximum depth at which groundwater pollution is encountered. <br /> In the event that laboratory analytical tests show that soil and groundwater samples <br /> collected in this investigation did not delineate the extent of contamination to non- <br /> detect, we may require Chevron to conduct additional sampling. Chevron should <br /> consider screening soil samples in the field using a photo-ionization detector, and <br /> collecting depth-discrete grab groundwater samples at greater depths. <br /> 2. Previous laboratory analytical results showed thzit there are elevated concentrations <br /> of petroleum hydrocarbons in soil in the area where sampling is proposed, but the <br /> Work Plan does not include laboratory analysis of soil samples. Based on these <br /> documented results, we strongly suggest that Chevron revise its proposed sampling <br /> program to include the submittal of soil samples for laboratory analysis. The data are <br /> needed to laterally delineate the contamination in the vadose zone, and may also be <br /> critical for calculating the mass of contamination in soil and assessing ecological and <br /> health risks as it becomes necessary to evaluate future remedial or eventual site <br /> closure alternatives. <br /> 3. The laboratory method identified on Page 5 may be erroneous. The correct <br /> laboratory analytical method for tetraethyl lead (TEL) and tetramethyl lead (TML) is <br /> Hazardous Materials Laboratory (HMQ 939-M. <br /> 4. It is not clear whether comparing the chromatograms from the laboratory analytical <br /> results to known standards would serve to elucidate the origin of the contaminants. <br /> Chevron and Central Valley Water Board staff have compared chromatograms <br /> generated from a previous sampling event to standards. The comparisons show that <br /> the weathered residual product generates chromatograms that are distinctly different <br /> than the original product and may not match standards. Instead of comparing the <br /> chromatograms to a known standard, we request that Chevron submit the laboratory <br /> analytical results of equipment blanks for each media and all standards used to <br /> create the respective calibration curves for the analytical results. <br /> The concerns addressed in the comments above prevent us from concurring with the <br /> Work Plan. By 5 November 2010, please submit a revised Work Plan that resolves <br /> these comments. <br />