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TAwLE 1 - CHECKLIST OF REQUIRED DATA <br /> FOR NO FURTHER ACTION REQUESTS AT UNDERGROUND TANK SITES <br /> Site Name and Location: Former Unocal Station#5421, 7303 Pacific Ave., Stockton, San Joaquin Co. <br /> Y 1. Distance to production wells for municipal, domestic, agriculture, industry Municipal well located approx. 114-mile <br /> east(downgradient)of the site. Several <br /> and other uses within 2000 feet of the site; <br /> other wells located cross/up gradient. <br /> 0 2. Site maps, to scale, of area impacted showing locations of former and existing tank systems, See closure report. <br /> excavation contours and sample locations, boring and monitoring well elevation contours, <br /> gradients, and nearby surface waters, buildings, streets, and subsurface utilities; <br /> Q 3. Figures depicting lithology(cross section), treatment system diagrams; Monitoring well borings and additional soil <br /> borings logs are included in various docs. <br /> EYD 4. Stockpiled soil remaining on-site or off-site disposal(quantity); approximately 3,180 cubic yards of soils was disposed <br /> of at three different landfilWhaz waste locations. <br /> a5. Monitoring wells remaining on-site, fate; 4 monitoring wells remain on-site.Destruction permit applications have been <br /> - submitted to SJCEHD for approval of well decommissioning. ^ <br /> 0 B. Tabulated results of all groundwater elevations and depths to water; All groundwater monitoring data was included in <br /> closure report. <br /> 7.Tabulated results of all sampling and analyses: <br /> Al!sampling results are present In the Closure Report, <br /> F Detection limits for confirmation sampling <br /> FN Lead analyses <br /> ID8. Concentration contours of contaminants found and those remaining in soil Soil contamination is well defined for both <br /> and groundwater, and both on-site and off--site: generations of tank excavations. The <br /> Y�Lateral andFYI Vertical extent of soil contamination lateral extent of groundwater impact is <br /> defined in relation to the first set of tanks; <br /> FN]Lateral and a Vertical extent of groundwater contamination however,is poorly def in rel to new tanks. <br /> 0 9.Zone of influence calculated and assumptions used for subsurface Soil overexcavation is the only remediation <br /> remediation system and the zone of capture attained for the soil and that was attempted at this site. <br /> groundwater remediation system; <br /> 0 10.Reports/information a Unauthorized Release Form FY-]QMRs(Dates) 1990- 1998 <br /> QWelland boring logs 0 PAR FRP Other(report name) Closure Report <br /> _YY -11.Best Available.:Technology.(BAT).used or an-explanation-for not using:BA-T,r giver--Ex used as the only remedial tech. <br /> NA 12.Reasons why background wash's unattainable using BAT; <br /> D13.Mass balance calculation of substance treated versus that remaining; Unknown mass remains in place in soils. No <br /> significant impact to groundwater presented. <br /> NA 14.Assumptions,parameters, calculations and model used in risk <br /> assessments, and fate and transport modeling; <br /> 0 15.Rationale why conditions remaining at site will not adversely Low,concentrations of contaminants were detected in I <br /> impact water quality, health, or other beneficial uses;and conf soil samples at approx.26'bgs. Historic high G W is <br /> at-35: Source is essentially removed <br /> NA 16.WET or TCLP results <br /> Sy., `"A„6 _ Comments:The information provided in the Closure report and by SJCEHD was evaluated in determining the site <br /> 1v klw status. Residual contamination remains in the soil at approximately 17'bgs. There is a low risk of impact to <br /> Date, groundwater from the UST activities at this site.Approximately 3,180 cubic yawls of contaminated soil were hauled + <br /> zb \°1\ from this site to landfills or haz waste disposal facilities. <br />