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COMPLIANCE INFO_JTD 12/4/2025
Environmental Health - Public
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EHD Program Facility Records by Street Name
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W
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WAVERLY
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6484
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4400 - Solid Waste Program
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PR0440004
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COMPLIANCE INFO_JTD 12/4/2025
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Last modified
2/20/2026 11:18:02 AM
Creation date
2/19/2026 8:47:04 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
JTD 12/4/2025
RECORD_ID
PR0440004
PE
4433 - LANDFILL DISPOSAL SITE
FACILITY_ID
FA0004517
FACILITY_NAME
FOOTHILL LANDFILL
STREET_NUMBER
6484
Direction
N
STREET_NAME
WAVERLY
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
09344002
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\cfield
Supplemental fields
Site Address
6484 N WAVERLY RD LINDEN 95236
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EHD - Public
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BRAY, RATHJE, AUGELLO AND MERRY D Seismic Design for Lined Solid-Waste Landfills <br />227GEOSYNTHETICS INTERNATIONAL S 1998, VOL. 5, NOS. 1-2 <br />Cover sliding . Analyze the landfill for localized cover sliding near the crest for the <br />design earthquake. Slope stability analyses indicate that the yield acceleration coeffi- <br />cient for localized cover sliding is 0.16. <br />1. Calculate the seismic loading,MHEACover : <br />MHA Rock <br />0.33g,NRF <br />1.05, and T sTm <br />1.3 from previous analysis <br />MHA Top[(MHARock)(NRF)]<br />0.9 to 1.1 (50% / 60%) (Figure 8 ) <br />MHA Top <br />(0.33g)(1.05)(0.9 to 1.1)<br />0.31g to 0.38g <br />MHEA Cover <br />(1.25)(0.31 to 0.38g)<br />0.39g to 0.48g <br />2. Estimate the seismically induced permanent displacements: <br />k max <br />MHEA Coverg <br />0.39 to 0.48, and k y <br />0.16 (given), so k yk max <br />0.33 to 0.41 <br />U <br />100 to 500 mm (from Figure 12, using 50 and 16% exceedance for Mw <br />7) <br />4 CONCLUSIONS <br />Landfill performance during recent earthquakes has been generally satisfactory. <br />However, one geosynthetic-lined landfill experienced significant damage, with two <br />tears observed in the HDPE geomembrane liner, and two unlined landfills were dam- <br />aged due to liquefaction-induced lateral spreading. Several landfills have experienced <br />moderate damage, evidenced by cracking in the interim soil cover at waste/natural <br />ground interfaces, cracking and limited downslope movement in cover soils, breaking <br />of gas extraction header lines, and a loss of power to the gas collection system. Back- <br />analyses of landfill performance during the Northridge earthquake in California have <br />provided exceptional opportunities to estimate the dynamic properties of solid-waste <br />fill and geosynthetic interfaces. However, due to the importance of evaluating these <br />properties, additional work is warranted. <br />Results from equivalent-linear and fully nonlinear seismic site response analyses in- <br />dicate that the dynamic response ofa MSWLFcan vary significantly due to reasonable <br />variations ofdynamic waste properties, fill heights, site conditions, and input rock mo- <br />tions. However, forthe base sliding case, the maximum seismic loading represented by <br />MHEA follows a well-defined trend.MHEA depends largely onthe initial fundamental <br />period ofthe waste fill,Ts =4H/Vs , andthe mean period,Tm ,andMHA ofthe inputrock <br />motion adjusted by the nonlinear response factor,NRF. Conversely, analytical results <br />indicate that the MHA calculated at the top of a landfill can vary significantly for rela- <br />tively modest variations in landfill configurations and input motions. Procedures that <br />first require an estimate ofthe MHA at the top ofa landfill to estimate the seismic load- <br />ingatthebaseofthelandfill arelimited bytherelatively largeuncertainty inestimating <br />MHA at the top of a landfill. <br />A rigid sliding block analysis can be significantly unconservative and should not be <br />used. However, asa seismic performance index, a reasonable (and generally conserva-
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