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ABLE I -CHECKLIST 0 TA <br /> F REQUIRED DA <br /> FOR NO FURTHER ACTION REQUESTS AT UNDERGROUND TANK SITES <br /> Site Name and LoLenz Property; 1648 Shaw Road,- Stockton, San Joaquin County(RB#390128) <br /> =Y 1. Distance to production wells for municipal, domestic, A sensitive receptor survey In 2000 identified no <br /> agriculture,industry and other uses within 2000 feet of the site, municipal supply and eleven domesticlagricultural wells <br /> within 2,000' the nearest wells are 900'S and 1250' K9. <br /> Y1 2. Site maps, to scale, of area impacted showing locations of Two 550-gallon USTs reportedly containing diesel were <br /> any former and existing tank systems, excavation contours and removed 10186 from the former Disco Warehouse. <br /> sample locations, boring and monitoring well elevation - Gasoline and lead scavengers 1,2-DCA and EDB were <br /> contours, gradients, and nearby surface waters, buildings, also reported in soil andlor groundwater samples <br /> streets, and subsurface utilities; <br /> _ <br /> 7_ <br /> V 1f 3. Figures depicting lithology(cross section); treatment system Site lithology consists of clay, silt,and sand to 134'$ the <br /> diagrams, total depth investigated. <br /> :ND I 4. Stockpiled soil remaining on-site or off-site disposal(quantity); The available reports do not describe the fate of the soil excavated during the USTs removal. <br /> Twelve monitoring wells(MW-1 through MW-12)and three SVE wells(VW-1 <br /> it <br /> M <br /> . Monitoring Wells remaining on-site, fate; <br /> Y 5through VW-3) will be properly abandoned. <br /> YJ 6. Tabulated results of all groundwater Depth to groundwater varied from 32'to 62'bgs. Groundwater flow <br /> directionvaried-in-all-compass directions-,^.S,,E,-and M;groundwater <br /> ele�atioris'inV d6plh�'t—owdt&, wadient varied from 0.001 to 0.011 ft/ft. <br /> 7. Tabulated results of a//sampling, Maximum soil boring concentrations on 12105 were TPHd,52,000 mg/kg;and on <br /> al <br /> and analyses: 9197 were TPHg, 14,000 mg/kg;toluene, 340 mg/kg;ethylbenzene,270 mg/kg;and <br /> xylenes, 1,600 mg/kg. In 4109,confirmation soil boring results were tPI40, <br /> byd Detection limits for confirmation'- 25 mg/kg;and TPHg,46 mg/kg- In 3105,typical groundwater monitoring <br /> sampling concentrations(MW-2)were TPHd,25,000 ug/L; TPHg,46,000 ug/L;benzene, <br /> 40 ugIL;toluene, 2,500 ug/L;ethylbenzene, 2,900 ug/L;and xylenes, 18,000 ugIL. <br /> FY� Lead analyses Maximum groundwater monitoring concentration for 1,2-DCA was 200 ug/L; while <br /> EDS was 21 uglL. In 8/08,all groundwater monitoring results were ND. <br /> y 8. Concentration contours of contaminants found and those remaining in soil and The extentof the iderifified <br /> groundwater, and both on-site and off-site: contamination is described in the <br /> reports. <br /> Lateral and <br /> Vertical extent of soil contamination <br /> F <br /> MY Lateral and ry-1 Vertical extent of groundwater contamination <br /> 9. Zone of influence calculated and assumptions used for subsurface remediation Soil Vapor Extraction was required by <br /> system and the zone of capture attained.for the soil and groundwater remediation the lead agency. <br /> system; <br /> 10.Reports linformation nY Unauthorized Release Form FYI QMRs 21 from-3/00 to 8/08 <br /> L_:_J <br /> fy-lWell and boring logs F7 PAR FYJFRP 0 Other CPT Rpt(1/02);SVE Pilot Test Rpt. (11102), <br /> Confirmation Soil Boring Rpt. (5109) <br /> 11.Best Available Technology(BA 7)used or an explanation for not using USTs removal, S VE soil treatment,and <br /> BATnatural attenuation. <br /> , <br /> -ft*lg BAT, <br /> Y 13.Mass balance calculation of substance treated In 5109, the calculated mass removed from soil was TPHg, 2219 <br /> versus that remaining; pounds. Estimated remaining soil mass was,TPHg, 169 pounds. <br /> 714. Assumptions,parameters, calculations and The April 2009 confirmation soil sample results(TPHd,25' bgs)reveal <br /> Y model used in risk assessments, and fate and that Region 2 ESLS(commercial,deep soil)were exceeded for direct- <br /> transport modeling; exposure and gross contamination. The consultant stated vapor <br /> intrusion is not a riskat the depth of contamination(25'bgs). The site <br /> is located in a commercially zoned area of Stockton. <br /> Y <br /> 15. Rationale why conditions remaining at site will Soil contamination reportedly is limited in extent. Land use is not <br /> I not adversely impact water quality, health, <br /> or other expected to change in the.foreseeable future. <br /> beneficial uses, and <br /> BY: JL8 Comments: Two 550-gallon USTs containing diesel were removed 10186 from the subject site, the former <br /> Disco Warehouse. Gasoline and lead scavengers 1,2-DCA and EDS were also reported in soil andlor <br /> Date: groundwater samples. Remediation by SVE resulted in a 93%reduction in estimated TPHg mass in soil. <br /> 6/4/2009 Based upon 21 quarters of groundwater monitoring showing a stable plume with declining concentrations to. <br /> NO, the limited extent of contamination remaining in soil,no foreseeable changes in land use(commercial), <br /> and the only TPHd ESLS exceedance for gross contamination and direct contact at a depth(25'bgs)where <br /> worker exposure and vapor intrusion are unlikely,Regional Board staff concur with San Joaquin County's <br /> Closure Recommendation. <br />