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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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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 (CLAI 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 />° 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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