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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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• • <br /> TECHNICAL MEMORANDUM <br /> Evaluation of Bed Ash Disposal <br /> Forward Landfill <br /> San Joaquin, California <br /> November 1, 2016 <br /> Page 3 <br /> between the beginning of 2010 and the end of 2015.1 WBP did not provide copies of the <br /> laboratory analytical reports and it is not known whether other constituents were analyzed. The <br /> WBP data summary is included in Appendix A. <br /> Table 1 provides a statistical summary of the analytical results and shows that no tested <br /> constituent exceeded its respective Total Threshold Limit Concentration (TTLC). Therefore, the <br /> bed ash is not hazardous with respect to TTLC criteria and the tested constituents. However, <br /> STLC Waste Extraction Test(WET) results showed that some of the samples met or exceeded the <br /> non-RCRA soluble hazardous waste criterion of 25 mg/L for copper. As shown by the WBP data <br /> included in Appendix A and summarized in Table 1,no other tested constituent exceeded its STLC <br /> regulatory threshold. <br /> BED ASH DELIVERY AND DISPOSAL <br /> Table 2 summarizes the amount of bed ash delivered and disposed at the landfill between the <br /> first quarter of 2014 and the fourth quarter of 2015 and includes WBP quarterly bed ash TTLC <br /> and STLC data for the same period of time. The bed ash delivered to the site by WBP was not <br /> segregated and was co-disposed with other wastes,including about 201,000 tons of ash from the <br /> Butte Fire. As indicated in Table 2,the amount of landfilled WBP bed ash was about 2,431 tons, <br /> or about one tenth of one percent of the total 1,683,604 tons of waste landfilled during the same <br /> period. All the bed ash was placed in Forward Units(FU) FU-04, FU-06, FU-08, FU-10, FU-13,and <br /> F-14 in the four areas shown in Figure 1 and no bed ash was placed in the pre-Subtitle D portion <br /> of the landfill. These units were all constructed with Subtitle-D liners that include leachate <br /> collection and recovery systems (LCRS)that convey the leachate to perimeter sumps. As shown <br /> in Table 2, bed ash accepted during the first three quarters of 2014 was disposed in Area 1 and <br /> Area 2. The amount placed in each area is not known; as a result, the evaluations summarized <br /> below assumed 50 percent of the bed ash received during this period was placed in Area 1 and <br /> 50 percent was placed in Area 2. <br /> FEASIBILITY OF EXCAVATION <br /> If it is assumed the ash was uniformly distributed,it would occur in layers less than 0.1-foot-thick <br /> at different elevations (or depths of burial) across the total of the four disposal areas shown in <br /> 1 CAM refers to the California Administrative Manual,also known as the California Code of Regulations(CCR). <br /> CCR Title 22§66261.24 specifies the 17 metals that can qualify waste as hazardous. <br />
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