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ARCHIVED REPORTS_XR0005133
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ARCHIVED REPORTS_XR0005133
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Last modified
9/23/2020 11:27:48 PM
Creation date
3/17/2020 4:51:31 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005133
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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y f� <br /> ti \� <br /> Second Quarter 1994 Status Report 2 <br /> Golden Grain Company, Manteca Bean Facility, 229 Moffat Blvd , Manteca, CA July 18, 1994 <br /> The water table elevations recorded on May 20, 1994, were used to prepare a potentiometnc surface <br /> map for the site (figure 2) The potentiometric surface elevations measured in the site groundwater <br /> monitoring wells decreased an average of 1 44 feet since the February 18, 1994, monitoring event <br /> The groundwater movement beneath the site flows generally to the north at an average gradient of <br /> 0 0014 foot per foot (ft/ft) The gradient at the southern portion of the site is greater and exhibits the <br /> effects of pumping from the groundwater extraction well on the site groundwater <br /> GROUNDWATER SAMPLING <br /> Groundwater samples were collected from 13 of the 14 monitoring wells on-site according to the <br /> LUFT guidelines Monitoring well MW-3 did not contain adequate groundwater to obtain samples <br /> Field data sheets from monitoring well gauging and sampling work are included in attachment 3 <br /> The samples were submitted under chain-of-custody protocol to GTEL Environmental Laboratories in <br /> Concord, California The samples were analyzed for benzene, toluene, ethylbenzene, and xylene <br /> (BTEX) and for total petroleum hydrocarbons-as-gasoline (TPH-g) using Environmental Protection <br /> Agency (EPA) Methods 5030/8015/8020 Historical and recent analytical data from groundwater <br /> analyses are summarized in table 2 The laboratory analyses reports and the chain-of-custody <br /> record for the water samples collected on May 20, 1994, are included in attachment 4 Maps <br /> showing reported values of dissolved TPH-g and benzene concentrations are Included as figures 3 <br /> and 4, respectively <br /> Of the 13 monitoring wells sampled in May 1994, dissolved TPH-g was detected in wells MWA, <br /> MW-2, MW-4, MW-5, MW-7, and MW-13 The dissolved TPH-g concentrations detected in <br /> groundwater samples from these wells were within the same range reported in the previous sampling <br /> event on February 18, 1994, except in the sample from well MW-13, where dissolved TPH-g was <br /> detected for the first time <br /> Benzene concentrations were detected in samples from wells MW-1, MW-2, MW-4, MW-5, MW-7, and <br /> MW-13 Concentrations of benzene less than 1 part per billion (ppb) were also detected in <br /> groundwater samples collected from wells MW-10, MW-11, and MW-14 The benzene concentrations <br /> detected in groundwater samples from these wells were within the same range reported in the <br /> previous sampling event on February 18, 1994, except for the following (1) benzene was detected at <br /> lower concentrations in wells MW-1 and MW-2 than had been previously reported, (2) benzene was <br /> detected for the first time in well MW-11 <br /> Monitoring wells MW-10, MW-13, and MW-14 are located upgradient and/or cross-gradient from the <br /> original source area for hydrocarbon concentrations on the site Groundwater monitoring data <br /> collected prior to the beginning of pumping from RW-1 (September 1992) indicate that these wells <br /> are also upgradient or cross-gradient from the site under nonpurnping conditions Groundwater <br /> 551OR024 020 <br /> GROUNDWATER <br /> TECHNOLOGY,INC <br />
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