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ARCHIVED REPORTS_XR0005114
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3500 - Local Oversight Program
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PR0545566
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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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i <br /> Closure Report 21 <br /> Golden Grain Manteca Bean Facility,299 Moffat Boulevard,Manteca,California July 16, IM <br /> from um test results and an average aquifer thickness, b, of 25 feet The n,value used in the <br /> pump 9 q <br /> model simulations, 0 40, is an average of the effective porosities for soil samples collected at the <br /> site The hydraulic gradient value used in the model simulations, 0 001 ft/ft, is based on groundwater <br /> level data for the site The calculated seepage velocity, vāā is equal to 0 1 foot/day This means <br /> 1 groundwater beneath the site is only moving about 37 feet per year(ft/yr) <br /> 5 2.2 Dispersion <br /> Dissolved contaminants also spread as they move with the groundwater This process, called <br /> hydrodynamic dispersion, is a combination of two basic processes, molecular diffusion and <br /> mechanical dispersion The overall result of hydrodynamic dispersion is the dilution of contaminant <br /> ' pulses and the attenuation of concentration peaks,the maximum concentrations diminish with <br /> increasing distance from the source In most cases the contribution of diffusion to solute transport is <br /> minimal, and can be neglected <br /> Mechanical dispersion, also known as mechanical , results from variations in groundwater <br /> p mixing, <br /> velocity within a porous medium caused by frictional forces, variations in pore geometry, and <br /> tortuosity of the porous medium which causes fluctuations in the local flow direction relative to the <br /> mean flow direction The coefficient of mechanical dispersion, D, is a function of the seepage <br /> velocity, vāā and the distance from the contaminant source, and is expressed as <br /> ' D = (vw)(d) <br /> where the constant of proportionality,termed the dispersivity, d, depends on the structure of the <br /> ' porous medium and vanes with the distance traversed Longitudinal dispersivities are generally on <br /> the order of 30 to 300 feet (Gelhar 1992) Dispersion in the direction of flow Is often observed to be <br /> 1 markedly greater than dispersion in the directions transverse to the flow The BIOPLUME model <br /> requires both a longitudinal and transverse dispersivity For the model simulations an estimated <br /> longitudinal dispersivity, d,, of 30 feet and transverse dispersivity, dT, of 3 feet were used <br /> ' 5 2 3 Sorption <br /> Sorption refers to the partitioning of a contaminant between the liquid and solid phases in a porous <br /> medium The term includes the processes of adsorption, ion exchange, colloid filtration, reversible <br /> ' precipitation and irreversible mineralization (Freeze and Cherry 1979) Of these, adsorption is the <br /> . dominant process Adsorption is defined as the transfer of contaminants from the liquid phase to the <br /> ' 4202M3.CR <br /> FLUOR DANIEL GTI <br />
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