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ARCHIVED REPORTS_2013_9
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ARCHIVED REPORTS_2013_9
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Last modified
7/17/2020 3:53:43 PM
Creation date
7/3/2020 10:57:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_9
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2013_9.tif
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EHD - Public
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With the exception of the iterative moisture contents described below, all soil and refuse <br /> parameters used in modeling the Forward Landfill LCRS are default values selected from <br /> the HELP program as typical for municipal solid waste landfills. Weather data was <br /> synthetically generated by the program for the Stockton area and corrected for the <br /> latitude of the Forward Landfill facility, yielding an average annual rainfall of <br /> approximately 15.8 inches. <br /> As a conservative measure, the HELP modeling that was completed for the project <br /> anticipated that the subgrade(liner) gradient beneath all development areas would be 2%, <br /> and that yearly thickness of refuse would be no greater than 10 feet. While wastes that <br /> are initially placed in landfills are typically dry,with a moisture content that is well <br /> below their field capacity(moisture holding capacity), for the Forward Landfill leachate <br /> generation analyses, as a conservative measure, it was assume that the upper 10-foot <br /> refuse section in each yearly simulation would exist at its field capacity. The moisture <br /> content for the underlying refuse layers was manually specified for each yearly <br /> simulation based on the results that were calculated for the previous year. As additional <br /> conservative measures,runoff was assumed to be impeded by a"fair stand of grass," <br /> though, for simulating transpiration, a bare ground(daily cover) condition was assumed. <br /> Current estimates are that the expanded Forward Landfill may operate for approximately <br /> 20 years. The HELP simulations were run for a period of 30 years: 20 years of active <br /> refuse disposal and 10 years of post-closure period with final cover and no positive or <br /> negative flux through the landfill's geomembrane cover. The simulation conservatively <br /> ignored placement of intermediate cover soils, and assumed that a one-foot thick LCRS <br /> drainage layer would be placed at a 2%gradient on top of a geomembrane layer at the <br /> base of refuse. LCRS collection pipe was assumed to exist on 200-foot centers. <br /> Model Results <br /> The average peak daily leachate that was calculated to be generated in a one-acre area <br /> with the greatest anticipated refuse thickness is approximately 397 cubic feet. As shown <br /> on the charts included in this section(Figures D-1 and D-2), this volume was generated <br /> after the first simulated year of refuse placement. Within the simulated one-acre landfill <br /> area, the average peak daily leachate generated is about 4000 gallons or.0045 cubic feet <br /> per second (cfs). The maximum peak daily head on the liner system was calculated to be <br /> approximately 1.6 inches. Accordingly,the 200-foot spacing of the LCRS appears more <br /> than adequate to keep less than one foot of leachate head on the liner. <br /> LCRS Pipe Capacity <br /> Since the largest tributary area within the planned new liner system is approximately 23 <br /> acres, the peak daily flow through leachate collector pipes to the leachate sumps will be <br /> approximately 0.10 efs. Recognizing that 27 CCR regulations require that the LCRS <br /> pipes be designed to accommodate double the peak daily leachate generation rate, the <br /> LCRS pipe at the facility should be designed to accommodate at least 0.20 efs. The <br />
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