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CID <br />. San Joaquin County Public Health Services <br /> May 26, 1995 (9347-1246) �-- .��7-1 <br /> Remediation Status <br /> During the 1989 tank replacement, approximately 1,058 cubic yards of soil containing <br /> petroleum hydrocarbons were excavated from around the former steel tank locations and disposed <br /> of off site The bulk of petroleum hydrocarbons In soil and separate phase hydrocarbons <br /> encountered during subsurface investigations and well monitoring at the site were beneath, and <br /> In the vicinity of, the former steel tank basin <br /> From December 1989 to April 1990, Delta Environmental Consultants, Inc (Delta), <br /> personnel hand-bailed separate phase hydrocarbons from well MW-2 on a weekly basis <br /> According to information contained in hugro's project files, Delta used electrically powered <br /> pumps to remove separate phase hydrocarbons from wells MW-2, MW-4 and MW-7 at various <br /> Intervals from April 13, 1990 to at least August 1991 The file information indicates at least 200 <br /> gallons of separate phase hydrocarbons were removed by Delta during pumping and hand bailing <br /> At SVE startup in September 1992, the total volatile hydrocarbon concentration quantified <br /> by laboratory analysis in the Influent airstream was 9,900 parts-per-million volume (ppmv) This <br /> concentration equates to an initial recovery of approximately 407 pounds, or 68 gallons per day <br /> (gasoline by weight = b lbs/gallon) Separate-phase hydrocarbons were present in <br />. venting/monitoring wells MW-2 and MW-4 at the time of SVE startup By September 1993 <br /> when pulsing of the vent system began, the influent hydrocarbon concentrations had dropped to <br /> about 200 ppmv Separate phase hydrocarbons have not been present in any of the wells since <br /> May 1993 The average concentrations of dissolved hydrocarbon compounds have also decreased <br /> in ground water during operation of the SVE system <br /> In September 1992, the ratio of benzene, toluene, ethylbenzene, and total xylenes (BTEX) <br /> to total hydrocarbon concentrations in the Influent airstream was approximately 27%, based on <br /> laboratory analysis By September 1993, this ratio dropped to approximately 10% Laboratory <br /> analysis of the influent air sample collected on March 27, 1995, indicates this ratio 1s currently <br /> about 7%, at a total Influent hydrocarbon mass concentration of 45 ppmv <br /> The March 1995 extraction rate corresponding to the soil vapor hydrocarbon concentration <br /> of 45 ppmv is less than one half of l% of the September 1992 rate of extraction The analytical <br /> data indicates the SVE system has effectively removed the bulk of hydrocarbons that can be <br /> remediated by vapor extraction Table I shows the hydrocarbon recovery data by the SVE <br /> system Table 2 shows historic air sampling analytical results The graphs shown on Figures 3, <br /> 4, 5, and b illustrate the trend of Influent hydrocarbon concentrations and extraction rates <br /> decreasing toward the asymptote <br /> Natural gas has been used as a supplemental fuel for operation of the oxidizer As <br />. hydrocarbon concentrations in the influent soil vapor decrease, the consumption of natural gas <br /> by the oxidizer Increases At startup in September 1992, the soil vapor hydrocarbon <br /> concentrations were approximately 9,900 ppmv, with virtually no natural gas consumption In <br /> 9347124611 r 3 - <br />