Laserfiche WebLink
UBLE 1 -CHECKLIST OF REQUIRED DATA O <br /> FOR NO FURTHER ACTION REQUESTS AT UNDERGROUND TANK SITES <br /> Site Name and Location: Copper Enterprises,12470 Locke Road, Lockford, San Joaquin County(Lustis Case 391082) <br /> Y 1. Distance to production wells for municipal, domestic, Geotracker shows six private wells within 2000 feet of the <br /> agriculture, industry and other uses within 2000 feet of the site. site. Distances and directions from site to private wells <br /> are not available on Geotracker. <br /> Y 2. Site maps, to scale, of area impacted showing locations of One 500-gallon gasoline UST was removed 8199. A <br /> any former and existing tank systems, excavation contours and concrete fuel oil bunker UST was closed in place 8199. <br /> sample locations, boring and monitoring well elevation Subsequently soil was overexcavated 11199 below the <br /> contours, gradients, and nearby surface waters, buildings, gasoline UST. <br /> streets, and subsurface utilities; <br /> Y 3. Figures depicting lithology(cross section), treatment system Site lithology was not described in reports. The total <br /> diagrams; depth investigated was approximately 15 feet. <br /> Y 4. Stockpiled soil remaining on-site or off-site disposal(quantity); approximately 30 cubic yards of over-excavated soil <br /> was removed, aerated, tested and remains(County <br /> approved)onsite(2100). Concrete bunker fuel product r <br /> and rinsate were transported offsite for dis osal. <br /> Y 5. Monitoringwells remaining on-site, fate; No monitoring wells were required or installed for this investigation. <br /> Y1 dwate <br /> -Depth°to-groundwater-wasreported•approximately-90-to-400- - <br /> feet-below- <br /> 6. Tabulated results of all grounr - <br />` elevations and depths to water,' ground surface(bgs). The reported regional groundwater flow direction <br /> is towards the south. <br /> 7. Tabulated results of all sampling In 8199, the maximum pre-remediation sail samples were TPHg, 690 mg/kg; <br /> and analyses: ethylbenzene, 0.15 mg/kg;and xylenes, 1.1 mg/kg. All confirmation soil borings <br /> f concentrations were ND in 8/99(under bunker UST)and in 11//99(under <br /> Detection limits for confirmation overexacavated gasoline UST). No groundwater samples were taken. -- <br /> sampling <br /> j QY Lead analyses <br /> 8. Concentration contours of contaminants found and those remaining in soil and The extent of the identified <br /> groundwater, and both on-site and off-site: contamination is described in applicable <br /> reports. <br /> _ Lateral and Y❑Vertical extent of soil contamination <br /> Lateral and FNIVertical extent of groundwater contamination ' <br /> 9. Zone of influence calculated and assumptions used for subsurface remediation Overexcavation to 15 feet bgs and onsite x <br /> system and the zone of capture attained for the soil and groundwater remediation aeration of soil were the required <br /> system; en ineered remediation. <br /> 10.Reports/information ❑Y Unauthorized Release Form ❑N QMRs <br /> WeIi and boring logs PAR IN Other <br /> f Y 11.Best Available Technology(BAT) used or an explanation for not using Removal of UST, overexcavation and soil <br /> BAT; aeration (gasoline), clean and inert fill <br /> __.(hunker). <br /> w Y 12. Reasons why background was<s unattainable No residual soil contamination detected on-site. Regional depth to <br /> BAT groundwater is approximately 90 to 100 feet. <br /> Y:1 13.Mass balance calculation of substance treated None calculated. <br /> versus that remaining; <br /> 714. Assumptions, parameters, calculations and No Region 2 ESLs were exceeded after remediation. <br /> model used in risk assessments, and fate and <br /> transport modeling; <br /> Y 15. Rationale why conditions remaining at site will Soil contamination was limited in extent and reported as remediated <br /> not adversely impact water quality, health, or other by aeration to ND levels. <br /> beneficial uses;and <br /> By: JL Comments: One 500-gallon gasoline UST was removed and one concrete fuel oil bunker was closed in place in <br /> l 8/99. In 8/99, the maximum gasoline UST pre-remediation soil samples were TPHg, 690 mg/kg;ethylbenzene, 0.15 <br /> Date: mg/kg;and xylenes, 1.1 mg/kg. No groundwater samples were taken. Subsequently soil was overexcavated below <br /> 4/21/2008 the gasoline UST. Approximately 30 cubic yards of over-excavated soil was removed, aerated, and spread onsite <br /> (2/00). All confirmation soil borings concentrations were ND in 8/99(under bunker UST) and in 11//99(after <br /> overexacavation of gasoline UST). Based upon the limited extent of contamination present in soil before <br /> remediation, no contamination detected after remediation, and the lack of a threat to groundwater and from soil vapor <br /> intrusion, Regional Board staff concur with San Joaquin County's Closure Recommendation. <br />