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ARCHIVED REPORTS_2001_2
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ARCHIVED REPORTS_2001_2
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Last modified
7/17/2020 3:53:22 PM
Creation date
7/3/2020 10:48:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2001_2
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_2001_2.tif
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EHD - Public
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With the exception of the iterative moisture contents described bed 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 />•a <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 cfs. 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 cfs. The <br />
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