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2200 - Hazardous Waste Program
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PR0505948
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Last modified
6/9/2020 2:01:51 PM
Creation date
6/3/2020 9:20:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0505948
PE
2227
FACILITY_ID
FA0007101
FACILITY_NAME
FORWARD INC LANDFILL
STREET_NUMBER
9999
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106003
CURRENT_STATUS
01
SITE_LOCATION
9999 S AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\HW\HW_2227_PR0505948_9999 S AUSTIN_.tif
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EHD - Public
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Table SA <br /> SUMMARY OF MULTIMEO INPUT PARAMETERS AND RESULTS <br /> DISPOSAL ALTERNATIVE 1 <br /> Forward Landfill,San Joaquin County,California <br /> PARAMETER UNITS AREA 1 AREA 2 AREA 3 AREA 4 BASIS <br /> Layer 1 no units 1.09 1.09 1.09 1.09 Based on Sharp-Hansen et al.(1990)Table 6-5 value for silty clay <br /> Layer 2 Organic Matteno units 2.68 2.68 2.68 2.68 Based on Sharp-Hansen et al.(1990)Table 6-5 value for sand <br /> _ <br /> Layer 1 percent 0 0 0 0 Conservative assumption(does not allow model attenuation) <br /> Layer 2 percent 0 0 0 0 Conservative assumption(does not allow model attenuation)--- <br /> Bulk <br /> ttenuation)_ <br /> BulkDensi <br /> Layer i g/cm 1.8 1.8 1.8 1.8 Site data(dry soil) <br /> Layer 2 g/cm3 1.7 1.7 1.7 1.7 Median site data(dry soil) <br /> Biological Decay Coefficient <br /> Layer 1_ er) <br /> 1/yr 0 0 0 0 Conservative assumption(not significant for copp <br /> La er 2 T 1/yr 0 0 0 0Conservative assumption not significant for copper) <br /> Groundwater Transport Parameters <br /> Aquifer Thickness m 12.2 12.2 12.2 _ 12.2 Site data(Andrew Eng/Herst Revised EFS and Annual Corrective Action Reports) <br /> Effective Porosity no units 0.35 0.35 0.35 0.35 Site data or estimate for uppermost saturated zone <br /> Bulk Density g/cm3 1.7 1.7 1.7 1.7 Median site data(dry soil) <br /> Mixing Zone Thickness m Derived Derived Derived_ Derived Derived by Model <br /> Mean Particle Diameter cm 0.02 0.02 0.02 0.02 Average of site grain size data <br /> Hydraulic Conductivity_ m/yr 1.89E+03 1.89E+03 1.89E+03 129E+03 Based on Victor Formation slug tests(2E-02 to 2E-03 cm/sec) <br /> Gradient _ m/m 0.002 OM 0.002 0.002 Median site data(see Figure 1) <br /> Seepage Velocity m/yr Derived Derived Derived Derived Calculated by Model <br /> Retardation Coefficient no units Derived Derived Derived Derived Derived by Model <br /> Vertical Dispersivity m Derived Derived Derived Derived Derived by Model <br /> ransverse Dispersivity m Derived_ Derived Derived_ Derived Derived by Model <br /> Aquifer Temperature _ °C 19 19 19 19 Average site monitoring data <br /> PH units _ 7.3 7.3 7-3 7.3 Median site monitoring data <br /> Fraction Organic Carbon no units 0 0 0 0 Conservative assumption(does not allow model attenuation) <br /> Radial Distance to Well in 213 165 332 205 Measure from center of assumed disposal area to closest downgradient monitoring well <br /> An le Off Gradient Axis degrees 0 0 0 0 Assumed to be directly downgradient from the source <br /> Well Screen Depth Fraction no units 0.23 0.23 0.50 0.50 Site-specific:ratio of screen length to depth of uppermost saturated zone <br /> Results <br /> Predicted Maximum Well Concentration mg/L 1.77E-07 5.60E-07 4.08E-08 8.21E-09 <br /> Transient Dilution Attenuation Factor no units 1.81E+08 5.72E+07 7.73E+08 6.21E+09 Ratio Initial Concentration:Detected Concentration <br /> Time Required to Reach Maximum yrs__ 22,000 11,600 20,600 41,200 <br /> ypical Copper,Detection Limit m L _ 0.0011 _0.0011 _ 0.0011 _0.0011 <br /> Detectable no units NO NO NO NO <br /> Multi le Re wired for Detection no units 6 211 1,965 26,981 133,983 <br />
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