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i <br /> Beacon Station No 641 September 28, 1998 <br /> Stockton California Remedial Testing Report <br /> The AST was initiated at approximately 2 30 p m after the VET had been operating for 3 3/4 <br /> hours The sparge compressor was initially operating at 12 4 pounds per square inch (PSI) <br /> and dropped to 11 PSI after 30 minutes of operation, and stabilized at approximately 7 2 PSI <br /> after 1 3/4 hours Pressure changes at wells VW-5 and VW-3 were almost immediate (15 to <br /> 30 minutes) after initiating the AST The vapor pressure in well VW-5 showed the most <br /> influence with a change from negative pressure induced by the VET to a positive 2 2 inches <br /> of water column induced by the AST The pressure data is summarized on Table 1 <br /> DO concentrations were taken on May 27, 1998 prior to the initiating of any testing and <br /> periodically during the AST These DO concentrations were measured utilizing a Hanna <br /> Instruments Dissolved Oxygen Meter DO measurements were taken in monitoring wells <br /> MW-1, MW-2, MW-4, MW-5, and VW-1 Initial DO concentrations ranged from 2 7 to 3 8 <br /> parts per million (ppm) Additional DO measurements were taken during the AST mainly <br /> during the last half of operation These measurements showed an increase in concentrations <br /> in DO in all wells measured except well MW-4 The dissolved oxygen data is summarized <br /> on Table 3 <br /> Based on observations and measurements of DO and pressure changes, it appears that an <br /> effective radius of influence for air-sparging would be approximately 20 feet utilizing well <br /> SW-1 at a sparge pressure of 7 2 PSI This radius would encompass the main portion of the <br /> dissolved hydrocarbon plume beneath the,UST cavity and western dispensers <br />• VET / AST Discussion and Conclusions <br /> The VET perfonned indicates that soil vapor extraction will effectively remove <br /> hydrocarbons from beneath the site Based on the concentrations being extracted during the <br /> VET, the most cost-effective device for initial treatment of the airstream would be through a <br /> catalytic hydrocarbon destruction unit Following that form of treatment, at lower <br /> concentrations, the most cost-effective device would be activated carbon vessels Assuming <br /> the radius of influence to be 18 feet and that the existing vapor extraction wells will be <br /> utilized, the area that can be effectively treated by vapor extraction is shown on the Vapor <br /> Extraction Map (Figure 3) In addition, it appears that air sparging in conjunction with <br /> vapor extraction would be effective in remediating hydrocarbons in the groundwater, and the <br /> air-sparge vapor will be effectively captured b3 vapor extraction as depicted on the Air <br /> Sparge Map (Figure 4) <br /> Aquifer Pumping Test <br /> Field work was conducted on May 28 and 29 1998 Horizon conducted aquifer pumping <br /> tests by using a 4-inch diameter submersible pump to pump groundwater from monitoring <br /> well MW-5, and measuring drawdown in observation wells MW-1 MW-2, MW-4, VW-1 <br />• and VW-7 Automated data loggers were used to continuously record water level data in <br /> observation wells MW-1, MW-2 and MW-4 Horizon's Field Methods and Procedures are <br /> included in Attachment A <br /> 1641-21 rpt 4 HORIZON ENVIRONMENTAL INC <br />