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ARCHIVED REPORTS_XR0005114
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ARCHIVED REPORTS_XR0005114
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Last modified
9/24/2020 12:38:23 AM
Creation date
3/17/2020 4:38:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005114
RECORD_ID
PR0545566
PE
3528
FACILITY_ID
FA0005479
FACILITY_NAME
MANTECA BEAN CO
STREET_NUMBER
229
STREET_NAME
MOFFAT
STREET_TYPE
BLVD
City
MANTECA
Zip
95336
CURRENT_STATUS
02
SITE_LOCATION
229 MOFFAT BLVD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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t <br /> 6 <br /> Closure Report <br /> Golden Grain Manteca Bean Facility,299 Moffat Boulevard,Manteca,California July 16.1M <br /> 1 <br /> In summary, the estimated hydrocarbon mass In vadose zone sod (includes adsorbed phase and <br /> ' vapor phase) was approximately 3,000 lbs <br /> ' 2 2.2 Extent of Hydrocarbon Impacted Groundwater <br /> Results of groundwater samples collected during the Initial site assessment activities Indicated the <br /> presence of free-phase petroleum hydrocarbons and an associated dissolved-phase groundwater <br /> ' plume The distribution of total petroleum hydrocarbons as gasoline (TPH-g) and benzene detected <br /> in groundwater in June 1988 is illustrated in figures 10 and 11, respectively <br /> Free-phase hydrocarbons were measured in monitoring wells MW-1 through MW-6 on June 21, 1988, <br /> with a maximum thickness of 2 97 feet measured in monitoring well MW-2,which is adjacent to the <br /> former underground tank location Removal of the free-phase product from wells MW-1, MW-2, <br /> MW-4, and MW-5 began in June 1989 and continued until prior to implementation of the groundwater <br /> remediation system The removal of the free-phase product at the site was accomplished through a <br /> manual well bailing program, and through use of pilot test equipment used during the remedlation <br /> feasibility tests conducted at the site The manual bailing program was continued until free phase was <br /> no longer present at the site The manual bailing of free-phase product began in June 1989 and <br /> continued to April 1991 At that time, no measurable amounts of free-phase existed, however, a <br /> ' sheen was noted intermittently in some site monitoring wells Free-phase product was removed and <br /> placed in an aboveground storage tank at the site prior to proper disposal <br /> ' Figures 12 and 13 illustrate the distribution of TPH-g and benzene detected in groundwater as of <br /> June 1990 These figures illustrate the baseline conditions of the dissolved groundwater plume prior <br /> to implementation of site remediation work Dissolved-phase mass in groundwater at that time was <br /> estimated at 35 pounds At that time, the lateral extent of dissolved hydrocarbons in groundwater <br /> was concentne around the location of the former underground gasoline tank, with a radius of <br /> approximately 100 feet The highest dissolved petroleum hydrocarbon concentrations were detected <br /> in the on-site wells, with an average decrease in concentrations of approximately 730 parts per billion <br /> (ppb) per foot away from the former underground tank location The hydraulic gradient pnor to <br /> groundwater extraction was relatively low(0 001 ft/ft),which contributed to the low mobility of the <br /> ' groundwater plume <br /> The vertical hydrocarbon concentration gradient was determined from groundwater samples <br /> ' collected in June 1990 Monitoring well MW-2, screened in the upper sand zone, contained 73,000 <br /> ppb TPH-g and 28,000 ppb benzene Monitoring well MW-7, adjacent to MW-2, and screened in the <br /> FLUOR DANIEL GTI <br /> I <br />
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