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ARCHIVED REPORTS_XR0005121
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ARCHIVED REPORTS_XR0005121
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Last modified
9/23/2020 10:35:22 PM
Creation date
3/17/2020 4:44:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005121
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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i r <br /> Manteca Bean Facility, 229 Moffat Boulevard, Manteca, Caldomia October 22, 1992 <br /> Golden Grain Company Page 2 <br /> summarized in Table 1 The water table elevations for August 21, 1992, were used to prepare a <br /> potentiometnc surface map (Figure 1) <br /> Monitoring Well Gauging and Sampling <br /> Following well gauging, groundwater samples were collected from eight monitoring wells in <br /> I <br /> accordance with the LUFT guidelines The samples were submitted under a chain-of-custody <br /> manifest to Sequoia Analytical Laboratories in Sacramento, California Each sample was analyzed <br /> for benzene, toluene, ethylbenzene and xylenes (BTEX), and total petroleum hydrocarbons-as- <br /> gasoline (TPH-as-gasoline) by Environmental Protection Agency (EPA) methods 5030/8015/8020 <br /> Historical and recent analytical data are summarized in Table 2 The laboratory analyses reports, <br /> and the chain-of-custody manifest for the August 21, 1992, samples are included in Attachment I <br /> Maps of dissolved TPH-as-gasoline and benzene concentrations are included as Figures 2 and 3, <br /> respectively <br /> I <br /> The potentlometric surface elevations in the site-related groundwater monitoring wells decreased in 9 <br /> of the wells an average of 2 56 feet since the last monitoring event conducted on May 21, 1992 <br /> • Wells MW-1 through MW-6 were dry Groundwater beneath the site flows approximately north- <br /> northeast at an overall gradient of 0 0015 The gradient at the southern end of the site is more steep <br /> than the gradient in the central and northern portion of the site Monitoring data from the last <br /> quarter (5/21/92) reported a sheen of separate phase petroleum hydrocarbons in MW-4 During this <br /> quarter, no separate phase petroleum hydrocarbons were detected in MW-4, due to lower <br /> groundwater elevations resulting in wells 1 through 6 being dry <br /> Of the eight monitoring wells sampled on August 21, 1992, dissolved TPH-as-gasoline was detected <br /> only in groundwater samples from MW-7 and MW-14 at concentrations of 6,600 and 68 parts per <br /> billion (ppb), respectively Benzene concentrations detected in MW-7 were 2,100 ppb and in MW-14 <br /> they were 0 5 ppb Concentrations of hydrocarbons detected in MW-14 this quarter however are not <br /> consistent with past sampling results Past laboratory results from groundwater samples of MW-14 <br /> for the last three quarters have been below detection limits MW-14 is located across Moffat <br /> Boulevard from the site and lies upgradient from the original source area on site <br /> Trace concentrations of toluene and xylenes from laboratory analysis were detected in groundwater <br /> samples from MW-9 and in one field blank sample Levels in these two samples were very low and <br /> indicate no significant change to site conditions The effect of trace amounts of hydrocarbons <br /> detected in the field blank may indicate that sample results with detected hydrocarbons are actually <br /> lower by 18 ppb toluene and 12 ppb xylenes Two possible explanations for these trace amounts <br /> . of hydrocarbons in the field blank result from slight contamination during handling Concentration <br /> levels this low indicate that, trace amounts of hydrocarbons, from contact source during field work, <br /> �L � CROUNDWA'TER <br /> �n TECHNOLOGY INC <br /> I <br /> I <br />
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