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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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0 0 <br /> TECHNICAL MEMORANDUM <br /> Evaluation of Bed Ash Disposal <br /> Forward Landfill <br /> San Joaquin, California <br /> November 1, 2016 <br /> Page 7 <br /> per unit area was calculated using the Giroud (1997) equation summarized in Table 3.4 Principal <br /> assumptions incorporated into these calculations included: <br /> • A constant leachate head of 1 foot (the maximum allowable head for Subtitle D liner <br /> systems) is always present on the liner; <br /> • Two circular 0.35-cm diameter defects are present in each unit area; <br /> • Continuous contact between the geomembrane and clay was assumed; and <br /> • The CCL is 2-feet-thick and has a saturated hydraulic conductivity of 1E-'cm/sec. <br /> As indicated in Table 3,the unit 1-acre leakage rate calculated by this procedure (QAi in Table 3) <br /> was 3.17E-6 meters per year (m/yr). For the case of bed ash disposal at Forward Landfill, and <br /> other factors being equal, the leakage rate and the time required to deplete the soluble copper <br /> in the bed ash will depend on the location and thickness of the ash within each of the areas shown <br /> in Figure 1. Because the actual disposal locations and ash thicknesses within each area are not <br /> known, two alternative disposal scenarios were considered to reasonably represent bed ash <br /> leaching potential and rates of leakage: <br /> • Disposal Alternative 1 assumed the bed ash was placed in a continuous uniform layer <br /> across the entire disposal area (Table 4A); and <br /> • Disposal Alternative 2 assumed the bed ash was sequestered in each disposal area in an <br /> approximately 2-foot-thick lift (Table 4B). <br /> The time required to deplete the source was approximated based on the median total copper <br /> concentrations,estimated leaching factors,and median STLC copper concentrations summarized <br /> in Table 2 and the annual average precipitation for the site area. As summarized below, the <br /> results of these analyses indicate a significant higher leakage rate is associated with Alternative <br /> 1. However,the time required to deplete the available copper from the bed ash is much shorter <br /> than the time required to deplete the relatively thicker source associated with Alternative 2: <br /> 4 The assumption of circular defects is not particularly important;similar results are obtained if rectangular or <br /> square defects are assumed. <br />
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