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� r`'-4BLE 1 -CHEGKLiST C1F REQUIRED DATAQ � <br /> FOR NO FURa..,,R ACTION REQUESTS AT UNDERGROUND UNK SITES <br /> Site Name and Location: City of LathroplDalwinder Dhoot,15688 Harlan Rd.,Lathrop,San Joaquin County(Case 391176) <br /> Y IDistance to production wells for municipal, domestic; According to Geotracker,there are no active public wells <br /> -dg _ <br /> culture; industry and other uses within 2000 feet of the site: within%mile of site. Oakwood Lake WaterDistrict <br /> Subdivision provides public water to the area. <br /> 2. Site maps,to scale,of area impacted showing locations Two 500-gallon unknown contents USTs and associated <br />! of any former and existing tank systems, excavation piping were removed from the site,located on the property <br /> contours and sample locations,boring and monito"ring well border of the City street and the new Best Western motel, j <br /> elevation contours,gradients, and nearby surfacer waters during construction in 4107. The tanks-were abandonedin <br /> buiJdin s streets and subsurface utilities; ince at a former WJ ins Market in me 1960's: <br /> Y 3. Figures depicting lithology(crass section) treatment Site lithology consists of clay,silt,and sand to <br /> t <br /> system diagrams; 15 feet,the total depth investigated. ' <br /> s <br /> Y 4. Stockpiled soil remaining on-site or off-site disposal(quantity); Approximately 45 cu.yds. of contaminated soil was <br /> removed and transported to Forward Landfill in <br /> Manteca. <br /> Three monitoring wells(M W-1 through;MW-,3)remaining on-site will be f <br /> Y 5. Monitoring wells remaining on-site; fate; propertyabandoned. <br /> 6. Tabulated results of all groundwater Depth to,groundwater varied from 11 to 12 feet below ground surface(bgs). <br /> elevations and depths to water, Thetgroundwater gradient varied from 0.004 to 0.005. The downgradlent <br /> groundwater flow direction was towards the northwest. .- <br /> y=T,-•-Tabulated•results-oaf-all-sampling -Maximum-confirma#ion:soil concentration-{4ItfT)-was-T.PHd,21-mg&g.-4 n-41{18,-soil--• <br /> and analysos: boring after results were all ND. Maximum grab groundwater concentrations <br /> during over-excavation(5/07)were TPHg, 7,900 ug1L;TPHd, 16,000 ugIL benzene; <br /> Detection.limits forconfimtation 140 ug1L;1toluene,33 ug/L;ethylbenzene,33 ug1L ;andxylenes,200 ugIL. In 12/08, <br /> I the maximum groundwater monitoring result was TPHd,74 uglL. <br /> sampling <br /> QY Lead analyses <br /> 8. Concentration contours of contaminants found and those remaining in soil and The extent of the idetred , <br /> j groundwater, and both on-site and gaff-site: contamination is shown in -, <br /> applicable reports. <br /> Lateral and L1/'vertical extent of soil contamination <br /> Lateral and Vertical extent of groundwatercontamina tion <br /> 9.• Zone of influence calculated and assumptions used forsubsurface remediation An engineered remediation was <br /> system and the.zone:of capture attainted for'the sail and groundwater remediation: not required by:the.regulatory <br /> system; agency, <br /> MY P � <br /> 10.Deports 1information U Unauthorized Release Form G?.! QMRs`(3 from 44/08 to 12108) i <br /> f <br /> Well-and bonng::logs PAR FRP Other; <br /> Y 11.Best Available Technology(BAT)used or an eXplanatian for not using BAT; Removal of USTs,over-excavation,And <br /> !I natural attenuation. <br /> 12. Reasons why background wasfs unattainable;)usin BAT Limited soft contamination remains on-site. <br /> r The consultant did not estimate contaminatronrenraining <br /> 13.Mass balance calculation of substance treated'Versus that <br /> remaining; In soil or groundwater. <br /> - 14:=Assumpptionsy aiatneters>-ealsulations-and-m6det-used-inm«_No.Region.2.ESLs_wereexceeded for�sorl_samptes-Site 4 ... <br /> Y �• <br /> nsk-assessments,and,fate and transport modeling; is a City s#reetlsidewalkl►andscape;and larrtd use <br /> {commercial)is not expected to change:h tha: <br /> foreseeable future. <br /> Y:5 15; Rationale:why:conditions remaining at site wrlflnot adversely Sol/and groundwater contamination are limltent l0 extent <br /> impact water+Tualtty,..hea1#h;..oro1her beneficial uses;and Results of 3 quarters of groundwater monftring:show a <br /> decreasln trend in concentrations. <br /> 8y: <br /> JAR Comments Two 500-gallon USTs and associated piping were removed from subject site,,located on the <br /> property border.of the city streets nal.the new Best Western motel,during construction in 4107.The tanks were <br /> Date. abandoned in pieat <br /> ce .a forrrter Wiggans Market in the 1960's. Maximum confirmation soli+concentration{4100 <br /> 312512009: wes 7'PHd,21;nrglkg. In4104;.soil boiling after results were all ND. Maximum grab grounrdwaterconcentratiorrs <br /> during over excavation(&07)were T,P,Ng, 7,900 ug/L;TPHd 10,000 ug& benzene,f40.ug1L,foluene,..IuglL; <br /> etllylbenzene,341 ug/L.;and xylenes, 200 ug1L. in 12(08, the maxftum groundwater monitoring resin#Was <br /> TPHd,,74:0glL. Based upon 3;quartsh of declining groundwater concentrations,:no reported threat from vapor ; <br /> lrrtruslon,no anticipated threat to sensitive receptors,no anticipated changes to.land use(commercial),and t <br /> *9 limited+sx nt of contamination plesent In soil and groundwater,Re4�ional:l3oard stili°concur with ySan <br /> Jrlecicrincounty's closure Recommendation. <br /> }: J <br />