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ARCHIVED REPORTS_2011_27
Environmental Health - Public
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ARCHIVED REPORTS_2011_27
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Last modified
7/17/2020 8:38:02 PM
Creation date
7/3/2020 10:56:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011_27
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_2011_27.tif
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EHD - Public
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0- TABLE 2- SOILS ENGINEERING PROPERTIES USED FOR MODELING. <br />Soil Properties <br />Alternative Final Cover <br />Mixture at 10% <br />Compacted Relative Density <br />90% <br />Sat. Permeability cm/sec (degraded on-site soils <br />3.30 x 10' <br />Optimum Moisture Content <br />16.8 <br />Dry Density PCF <br />99.5 <br />Li uid Limit <br />NA <br />Plasticity Index <br />NA <br /><#200 Sieve <br />76 <br /><5 Micron % <br />30 <br />U.S.C.S. Classification <br />CL <br />Remolded Bulk Dry Density cm <br />1.56 <br />Cam bell's A Coefficient <br />-4.89 <br />Campbeffs B Coefficient <br />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 />IM <br />C:i2O9SA082WORWARD/ForwardCOVERDOC\7/13/2005 <br />Geologic Associates <br />
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