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CERTIFIED ANALYTICAL REPORT <br /> The certified analytical report generated by the laboratory is the official <br /> document in which they issue their findings. The certified analytical report <br /> should be closely reviewed when samples are taken from below waste oil tanks <br /> as any detection of the EPA halogenated and purgeable aromatic compounds may <br /> be grounds for requiring further action. The certified analytical report is <br /> included as an attachment at the close of this report. <br /> GENERAL ADVISORY ON POSITIVE RESULTS <br /> Though our firm specializes in sampling, monitoring and documentation, rather <br /> than interpretation and remediation, we have been asked by the engineering <br /> staff of the Regional Water Quality Control Board to include in our reports <br /> an advisory section outlining the general type of additional actions which <br /> may be required when contamination is found. This advisory is not intended <br /> to characterize conditions at this particular site or replace the services of <br /> a consulting firm specializing in the investigation, characterization and <br /> remediation of such conditions as may exist. Rather, it is intended to <br /> advise you that such additional actions may be required even though some time <br /> may elapse before you are contacted by one of the interested regulatory <br /> agencies. <br /> In Region 2 (which is regulated by the San Francisco Regional Water Quality <br /> Control Board), the thresholds are readily defined in the Board's <br /> publication, Guidelines For Addressing Fuel Leaks. According to this <br /> document, soil which has less than 100 parts per million total petroleum fuel <br /> hydrocarbon (TPH) contamination does not generally require immediate <br /> additional action. Board engineers emphasize that this does not mean that <br /> some action might not be required in the future. Still, the site is assigned <br /> a low priority unless it is situated in an area of high hydrogeologic <br /> concern. <br /> The detection of more than 100 ppm TPH in the native soil beneath a tank is <br /> generally considered grounds for requiring an additional investigation in the <br /> form of soil borings and installation of at least one groundwater monitoring <br /> well followed by periodic monitoring. The detection of 1000 ppm TPH is <br /> usually viewed by the Board as an unacceptable level of fuel saturation which <br /> will mandate excavation of the effected ground down to the furthest <br /> practicable reach of conventional excavating machinery followed by soil <br /> borings and installation of groundwater monitoring wells. <br /> Other regions use different standards for determining when a groundwater <br /> investigation will be required. For example benzene is often used in lieu of <br /> TPH. Even very low levels of benzene are often seen as grounds for requiring <br /> a subsurface investigation. This criteria may be relaxed or stiffened <br /> depending on the location of the site in relation to different groundwater <br /> systems, the depth to water, type of soil, and the concentrations of benzene <br /> involved. <br /> Sampling Report 88306-M-2 AL WILLIAMSON page 6 <br />