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ARCHIVED REPORTS_2005_2
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ARCHIVED REPORTS_2005_2
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Entry Properties
Last modified
7/17/2020 3:53:23 PM
Creation date
7/3/2020 10:49:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2005_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
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2005_2.tif
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EHD - Public
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TABLE 2-SOILS ENGINEERING PROPERTIES USED FOR MODELING <br /> Soil Properties Alternative Final Cover <br /> Mixture at 10% <br /> Compacted Relative Density 90% <br /> Sat.Permeability cm/sec)(degraded on-site soils) 3.30 x 10'6 <br /> Optimum Moisture Content 16.8 <br /> Dry Density(PCF) 99.5 <br /> Liquid Limit NA <br /> Plasticity Index NA <br /> <#200 Sieve 76 <br /> <5 Micron % 30 <br /> U.S.C.S.Classification CL <br /> Remolded Bulk Dry Density( /cm) 1.56 <br /> Campbell's A Coefficient -4.89 <br /> Campbell's B Coefficient 8.403 <br /> 4.2.4 CLIMATIC CONDITIONS <br /> Precipitation - Another critical element in modeling cover performance using LEACHM <br /> involves identification of total daily precipitation, as well as the time and rate of water <br /> application. For each rain event, LEACHM calculates the maximum time period allowed <br /> for infiltration as the specified quantity of water to be applied divided by the application <br /> rate. Water, which has not entered the soil profile at the end of the application period, is <br /> assigned to an excess runoff term and included in the mass balance calculations. The <br /> matric potential of the soil and the unsaturated hydraulic conductivity of the soil thus <br /> limit infiltration into the profile at the time of water application. In other words, <br /> infiltration is limited by the ability of the soil to take water. <br /> Since positive drainage will always be maintained on the landfill surface, no ponding of <br /> rain or irrigation waters was included in the analyses. <br /> The enclosed analyses of a non-prescriptive cover at the FSL were performed utilizing <br /> precipitation data recorded at the Western Regional Climate Center's Stockton Station for <br /> the years 1993-2002. The magnitude and duration of the rainfall events were estimated in <br /> a fashion believed to conservatively represent typical anticipated application. This <br /> included defining the time of day for water application to be 0.4 days (9:36 am) and a <br /> water application rate of 60 mm/day. <br /> Evapotranspiration- LEACHM requires mean weekly pan evaporation data from which <br /> daily potential evapotranspiration(DPET) is calculated as one-seventh of the weekly total <br /> pan evaporation. Daily potential transpiration is calculated by multiplying the DPET by a <br /> crop cover fraction. Daily potential evaporation is then calculated as the difference <br /> between DPET and potential transpiration. For modeling purposes, LEACHM assumes <br /> that evapotranspiration starts at 0.3 days (7:12 a.m.) and ends 12 hours later at 0.8 day <br /> (7:12 p.m.). During this period, potential evapotranspiration is varied sinusoidally with <br /> -5- <br /> C:\2005-0082\FOR WARD/ForwordCOVER.DOC\7/13/2005 <br /> Geologic Associates <br />
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