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CORRESPONDENCE_2018-2020
Environmental Health - Public
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CORRESPONDENCE_2018-2020
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Last modified
4/17/2025 10:05:46 AM
Creation date
12/20/2021 12:36:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2018-2020
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
SITE_LOCATION
6484 N WAVERLY RD
P_LOCATION
99
P_DISTRICT
004
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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LCRS Design - Area 213 <br />Foothill Sanitary Landfill <br />TABLE 3 - FOOTHILL SANITARY LANDFILL 2017 LEACHATE DATA: AREA 2A <br />MONTH <br />GALLONS <br />COLLECTED PER <br />MONTH' <br />FLOW RATE <br />(GPD)' <br />FLOW RATE <br />(ft3/day) <br />FLOW RATE <br />(ft3/day/ac) <br />Dec <br />1,049,710 <br />33,765 <br />4514 <br />309 <br />Average <br />784,271 <br />25,723 <br />3,439 <br />236 <br />Max <br />1,512,510 <br />50,417 <br />6740 <br />462 <br />Area of Module 2A: 14.6 acres <br />Information provided by San Joaquin Public Works Department Solid Waste Division <br />From HELP analysis, peak leachate production is estimated to be 1,235 ft3 per acre per day <br />1 County supplied information <br />2January was not included in the average calculation as it appears to be anomalous <br />Based on the HELP modeling described above, the predicted peak daily lateral drainage for the <br />active cell condition is 0.34 inches, which converts to approximately 9,240 gallons per acre per <br />day. From the information presented in Table 3, the maximum daily collected leachate was <br />3,460 gallons per acre per day, which means the GDN can handle 2.7 times the peak 2017 <br />value. Thus, it can be concluded that using the Area 2A peak daily lateral drainage from the <br />HELP model predictions described above is reasonable and conservative relative to the leachate <br />volumes anticipated at the site. <br />5.0 ALTERNATIVE DRAINAGE LAYER DESIGN <br />5.1 Transmissivity <br />Title 27, Section 20340(b) requires LCRS systems to handle twice the anticipated maximum daily <br />leachate flow (i.e. factor of safety > 2). To satisfy this requirement, the design transmissivity <br />requirement of the GDN was evaluated using general GDN analysis methods described in the <br />GSE Drainage Design Manual (2007). <br />The factor of safety against failure of the drainage layer was calculated by multiplying the <br />required transmissivity (E)req) by published reduction factors for clogging (chemical and <br />biological) and material creep (compression due to loading), and also by a design factor of <br />safety. Multiplication by the reduction factors and design factor of safety results in the design <br />transmissivity (Odes). Odes was calculated as a function of the peak daily impingement rate (from <br />HELP analyses), the maximum drainage length to LCRS pipe, hydraulic conductivity, and slope of <br />the drainage layer. Transmissivity calculation sheets are included as Attachment 2 to this <br />report. The minimum design factor of safety used in the GDN capacity calculations was 2.0. <br />The specified transmissivity (Odes) of the GDN includes a design factor of safety of 2.0, and <br />results in a transmissivity of 7.1x10-4 m2/s at a vertical stress of 1,000 psf and 2.9x10-4 M2/s at a <br />vertical stress of 11,000 psf. The predicted maximum head of leachate on the liner system <br />Project No. ALI17.1254 1 LCRS Design <br />May 2018 <br />
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