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Ernesto Renteria, Jr. March 12, 2015 <br /> Pimentel Property Page 3 of 4 <br /> 1650 S. EI Dorado Street <br /> Stockton, CA 95219 <br /> uncertainty that the one vapor point sampled in the former dry cleaning area was near the point <br /> most likely to have been at a release point; the EHD is of the opinion that this uncertainty can be <br /> reduced by identifying the location(s) of the former dry cleaning equipment or increasing the number <br /> of sampling points in the former dry cleaning facility building footprint. It seems a bit surprising that <br /> the one soil gas sample not to contain detectable concentrations of PCE was the one collected <br /> within the suspected footprint of the former facility building. The EHD also recommends sampling <br /> along the former sewer line if it still exists and its location can be determined; the CVRWQCB also <br /> recommends videotaping the sewer line interior to identify potential release points to guide the <br /> selection of sampling points. <br /> The CVRWQCB thought the sample with a high leak-detector concentration should be resampled, <br /> with which the EHD concurs. The CVRWQCB also thought the three-foot soil gas sampling depth <br /> needed to be justified or the samples collected from the more commonly utilized five-foot sampling <br /> depth, which the EHD also recommends; the deeper, standard depth may help minimize the <br /> potential compromising of sample integrity by leakage of atmospheric air. Any additional soil gas <br /> sampling should incorporate a methodology for quantifying the effects of atmospheric leakage, if <br /> detected, on the analytical results. <br /> The soil and groundwater data collected from boring B3 shows that there was a release in the area <br /> of the suspected former UST system and the soil discoloration, odor and analytical data <br /> demonstrated that the boring was located in or near the point of release. The lack of detectable <br /> BTEX in the B3 soil samples is consistent with an aged, biodegraded petroleum fuel release, as is <br /> the lack of benzene and minimal toluene, ethylbenzene and xylenes in the B3 groundwater sample. <br /> However, the sample does show that groundwater was impacted by the release. As groundwater <br /> has been impacted, current practice is to determine the depth of the impact as well as the lateral <br /> extent. The depth, or vertical extent, of impacted groundwater has not been demonstrated, <br /> however, if it can be shown that the groundwater samples collected from B1, B2 and/or B7 are <br /> downgradient of B3 and are from the sandy interval encountered at 35 feet below surface grade <br /> (bsg) in B7, and deeper contamination is not encountered, the EHD will consider the lateral extent <br /> of impacted groundwater to be adequately demonstrated at this time. <br /> The EHD cannot issue a letter stating that the investigation of possible UST and dry cleaning <br /> releases is complete, poses minimal environmental or human health risks, and that further <br /> investigation is not necessary until the following items have been adequately demonstrated: <br /> • All data QA/QC elements have been reported and are satisfactory, <br /> • The soil gas sampling density in the former dry cleaning facility building footprint is sufficient <br /> for reasonable confidence that any releases from the equipment or plumbing have been <br /> detected; <br /> • The vertical and lateral extent groundwater impacted by the suspected UST release has <br /> been delineated; and <br /> • Currently known and any additional contamination encountered on the site does not pose a <br /> significant threat to human health or the environment. <br /> To address the items noted above, please submit a work plan to acquire the data needed to <br /> complete the site characterization. The EHD will review the work plan for adequacy and comment <br /> on it. Please include the analytical results for PCE on all tables of relevant data in future reports. <br />