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ARCHIVED REPORTS_2010_14
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ARCHIVED REPORTS_2010_14
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Last modified
7/18/2020 12:56:45 AM
Creation date
7/3/2020 10:55:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2010_14
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_2010_14.tif
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EHD - Public
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The GSE Drainage Design Manual Chapter 4-Design Methods And Concepts <br /> GRI-GC8 recommends using values in the range of 1.1 to 1.3 for biological clogging in the <br /> leachate collection system (see Table 4.4). The designer should evaluate the conditions <br /> anticipated in the landfill to select an appropriate value for the biological clogging reduction <br /> factor. In the absence of available information, the designer is urged to choose a conservative <br /> value(i.e., 1.3). <br /> GRI-GC8 recommends using values in the range of 1.1 to 1.3 for biological clogging in the <br /> leakage detection system(see Table 4.4).The designer should evaluate the conditions anticipated <br /> in the landfill to select an appropriate value for the biological clogging reduction factor. In the <br /> absence of available information,the designer is urged to choose a conservative value(i.e., 1.3). <br /> 4.3.4 Creep Reduction Factors, RFcR <br /> Performance transmissivity tests are typically conducted for up to 100 hours, as required by GRI <br /> test procedure GC8. The decrease in transmissivity with time levels off within 100 hours, and <br /> usually much sooner than that, indicating that much of the initial compression and intrusion has <br /> already taken place (see Figure 2.5). Reduction factor for creep,RFS% accounts for the decrease <br /> in transmissivity beyond the first 100 hours covered by the performance transmissivity test. The <br /> quality of the geonet core, including its structure, thickness, mass and density can have a <br /> significant influence on creep reduction factors. Table 4.5 presents creep reduction factors for <br /> geonets manufactured by GSE Lining Technology, Inc. Products from other manufacturers can <br /> have creep factors different from those given here. <br /> Regardless of the type of product, creep increases with increasing overburden stress. For this <br /> reason, creep reduction factors for cover applications (i.e., cover drainage and gas removal <br /> layers) are significantly smaller than those for liner system applications (i.e., LCRS and LDS). <br /> As shown in Table 4.5, a creep reduction factor of 1.1 is adequate for most cover projects. Creep <br /> reduction factors should be selected on the basis of normal stress for LCRS and LDS. A <br /> conservative value of creep reduction factors may be 2 for landfill liner systems with overburden <br /> stress of up to 15000 psf. <br /> Table 4.5 Creep reduction factors(RFm)for geonets manufactured by GSE Lining Technology, <br /> Inc., are'o and Allen,20041. <br /> Pressur=e,kPa: sk *tuatitractorR= . <br /> 48 1000 1.1 <br /> 240 5000 1.2 <br /> 478 10000 1.3 <br /> 7I8 15000 1.6 <br /> 4.4 Seepage Forces and Cover Soil Stability <br /> The selection of a geosynthetic drainage layer in the previous section (Section 4.3) was based <br /> solely on impingement rate (q;) and the resulting required transmissivity, O q. The use of <br /> Equation 4.24 for calculating allowable transmissivity would ensure that liquid head stays within <br /> the drainage layer, i.e., all percolation is adequately handled by the drainage layer. Relative to <br /> slope stability, this criterion is important to insure that no excess seepage forces need be <br /> considered when performing stability calculations. <br /> Page 4-16 <br />
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