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3500 - Local Oversight Program
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PR0543369
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
10/22/2018 4:50:11 PM
Creation date
10/22/2018 3:50:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0543369
PE
3528
FACILITY_ID
FA0013686
FACILITY_NAME
JOE WILSON CENTER MUSEUM
STREET_NUMBER
1141
STREET_NAME
ADAMS
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
23313020
CURRENT_STATUS
02
SITE_LOCATION
1141 ADAMS ST
P_LOCATION
03
QC Status
Approved
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EHD - Public
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€ �l a <br /> TABS 1 - CHECKLIST OF REQUIRED WTA <br /> . FOR NO FURTHER ACTION REQUESTS AT.UNDERGROUND TANK SITES <br /> Site Name and Location: Joe Wilson Center, 1141 Adams Street,Tracy,San Joaquin County <br /> ETI 1. Distance toroduction wells for munici al, domestic agriculture, As provided by the County, the nearest municipal well <br /> P A <br /> industry and other uses within 2000 feet of the site; is approximately 1,000 feet southeast of the site. <br /> 2. Site maps, to scale, of area impacted showing locations of former and existing tank systems; <br /> One 1,500-gallon fuel oil <br /> excavation contours and sample locations, boring and monitoring well elevation contours, UST was removed in 11/01. <br /> gradients, and nearby surface wafers, buildings, streets,and subsurface utilities,, Site maps are provided in <br /> 1� the UST Removal Report <br /> N❑ 3. Figures depicting lithology(cross section), treatment system diagrams; Soil investigation consisted of UST removal and <br /> overexcavadon of contaminated soils to 14 feet <br /> A soil profile was not required <br /> F714. Stockpiled soil disposed off-site(quantify); approximately eight tons of impacted soil was excavated from the <br /> tank pit and disposed it Forward Landfill. <br /> 4 <br /> 0 5. Monitoring wells remaining on-site, fate; Groundwater contamination was not identified,and monitoring wells were not <br /> installed. <br /> —7Tebulafed results of=all-roundwater elevations andile ihs fo wafer Mani rFng wells were not installed. First ff <br /> g p <br /> groundwater was identified at 14 feet in the tank pit <br /> Y 7.Tabulated results of all sampling and analyses: <br /> Maximum soil contamination only showed diesel at 10,000 mg/kg, <br /> I Defection limits for confirmation sampling which was later excavated and disposed off site. Lead was detected in <br /> soil at 14 to 24 mg/kg,which is within background concentrations for <br /> Lead analyses this area. Groundwaterlgrab samples from the tank pit were non- <br /> defect for all constituents including MtBE and fuel oxygenates. <br /> E] 8. Concentration contours of contaminants found and those remaining in soil !j <br /> and groundwater, and both on-site and off-site: Diesel impacted soil was excavated and <br /> Lateral and �� disposed o <br /> 9 Vertical extent of soil contamination off-site. Groundwater <br /> Lateral andF] Vertical extent of groundwater contamination contamination was not identified. <br />'f 09.Zone of influence calculated and assumptions used for subsurface Based on the limited contamination,site <br /> N A �° <br /> remediation system and the zone of capture attained for the soil and remediation beyond soil excavation and <br /> groundwater remediation system; disposal was not required. <br /> r <br /> 10.Reports/information lin Unauthorized Release Foran N� QMRs <br /> LJ � <br /> N❑ Boring logs EIPAR � FRP UST Removal Report, 1/2002 <br /> 11.Best Available Technology(BAT)used or an explanation for not using BA T. <br /> ii The'USTs and contaminated soils were <br /> removed. <br />[ Soil contamination was excavated andoff-site.disposed o -site. Groundwater <br /> Q 12.Reasons why background was/is <br /> unattainable using BAT; contamination was not identified. <br /> _ �--4.-... - -�,..:r -�^""E'.�'=c.rte--,-�—�_.-.--'•'•.'�W".�-�,�..:I�:..-.'�'. .:��„"•�'�._......._...._... <br /> Based on the removal of contaminated soils and no detectable roundwater <br /> 13.Mass balance calculation of substance , g <br /> contamination, an estimate of the remaining mass was not required. <br /> treated versus that remaining; I <br /> 14.Assumptions,parameters, calculations and madel used in risk Due to no idetectable groundwater contamination,a risk <br /> I" assessments, and fate and transport modeling; assessment was not required <br />!' 15. Rationale why conditions remaining at site will not adversely Contaminated soils were disposed off-site, and <br /> impact water quality, health, or other beneficial uses;and groundwater contamination was not identified. <br /> i! <br /> By. Comments:A 1,500-gallon UST was removed from the site on 29 November 2001. The former UST was used to store fuel <br /> MH oil for heating boilers that were taken out of service prior to November 2001. Soil contamination was identified during the <br /> UST removal of 12 feet, and 8.58 tons of impacted soil was removed and'disposed at Forward Landfill in December 2001. <br />'i The confirmation soil sample following overexcavation activities was non-detect for all constituents. Two groundwater grab <br /> Date: samples were collected from the tank pit excavation following overexcavafi'on activities and were non-detect for all <br /> I 315102 constituents including.MfBI=and fuel oxygenates at appropriate detection limits. The former UST site is in a parking lot area <br /> for the Joe Wilson Center, which has been repaved with asphalt. Based on the site investigation and excavation activities <br /> completed to date, Board staff concur with San Joaquin County's closure recommendation. <br /> r <br /> I� <br /> it . <br />
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