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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
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<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
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<br />   		system diagrams;   						15 feet,the total depth investigated.      				'
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<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,
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<br />   		10.Deports 1information  U Unauthorized Release Form   G?.! QMRs`(3 from 44/08 to 12108)    					i
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<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  ...
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<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.
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<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.
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