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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
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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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Gosure Report 23 <br /> Golden Grain Manteca Bean Facility,299 Moffat Boulevard,Manteca,California July 16,19% <br /> 5.2.4 Biodegradation <br /> ' Aerobic biodegradation Is the process of hydrocarbon removal by microorganisms in-the presence of <br /> oxygen Aerobic biodegradation can degrade benzene if dissolved oxygen is present In sufficient <br /> concentrations, usually greater than 1 to 2 mg/L(Chiang et al 1989) Dissolved oxygen <br /> concentrations in groundwater downgradient of the plume at this site range from 3 to 4 mg/L Data <br /> suggests that natural attenuation from aerobic biodegradation can occur at rates of 0 3 to 1 3 percent <br /> per day for BTEX compounds if an active microbial population is present and acclimated to the <br /> subsurface contaminant It can be assumed that intrinsic aerobic biodegradation is occurring at the <br /> site based upon evidence of reduced dissolved oxygen concentrations within the plume Dissolved <br /> oxygen concentrations in groundwater within the plume range from 1 to 2 mg/L A difference in pH <br /> between contaminated and uncontaminated groundwater is another indicator of biological activity <br /> ' (Buscheck and O'Reilly 1995) The pH of groundwater samples from within the plume is consistently <br /> lower than pH from samples downgradient of the plume Furthermore high concentrations of heavy <br /> metals and salts which may inhibit biodegradation are not present The average total dissolved <br /> ' solids concentration of groundwater at the site is 300 mg/L <br /> The BIOPLUME model can simulate the source of oxygen Into an aquifer in three ways the Initial <br /> dissolved oxygen in the uncontaminated aquifer, natural recharge of oxygen across the model <br /> y boundaries, and vertical exchange of oxygen from the vadose zone (reaeration) For the model <br /> ' simulations it was assumed there was no recharge across the model boundaries This is a <br /> conservative assumption because even though the groundwater seepage velocity is quite small, over <br /> ' time the groundwater beneath the site will be recharged by inflow from upgradient, oxygenated <br /> groundwater For the model simulations it was assumed there was no reaeration This is a <br /> conservative assumption because the seasonal fluctuation of the shallow water table beneath the <br /> site suggests that recharge from the surface does occur <br /> For the model simulations it was assumed there was a constant dissolved contaminant source of <br /> 780,ug/L benzene This is a conservative assumption because although there may be residual <br /> contamination in the vadose zone beneath the site, this source would also be diminishing over time <br /> ' due to biodegradation BIOPLUME is a saturated flow and transport model and cannot simulate <br /> conditions in the vadose zone Model simulations were run to evaluate the effect of a constant <br /> ' source versus no source <br /> Recent research has also indicated that biodegradation can occur under anaerobic conditions (Kuhn <br /> ' et al 1985 and McCarty 1994) Groundwater samples were collected at the site and analyzed for <br /> dissolved inorganic constituents such as nitrate, sulfate, and alkalinity, which can be used as <br /> ' 42020213 GR <br /> FLUOR DANIEL GTI �5- <br />
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