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ARCHIVED REPORTS_2005_6
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ARCHIVED REPORTS_2005_6
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Last modified
7/18/2020 5:41:08 AM
Creation date
7/3/2020 10:50:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2005_6
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_2005_6.tif
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EHD - Public
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4.4 MODELING RESULTS 0 <br />Modeling the performance of the low hydraulic conductivity barrier layer of a <br />prescriptive cover system constructed in an and and semi -arid climate is <br />particularly difficult because environmental stresses (desiccation and settlement <br />cracking) are likely to degrade the hydraulic properties of the low hydraulic <br />conductivity barrier layer over the long term. Consequently, modeling results <br />based on unstressed initial material properties will not be realistic. In fact, <br />academic investigations indicate that the saturated hydraulic conductivity of a <br />prescriptive cover system in a semi -arid to and climate can degrade by two to <br />three orders of magnitude within a period of a few years (Dr. Craig Benson, <br />personal communication). A similar condition is noted in the test results presented <br />herein where the initial remolded saturated hydraulic conductivity of the clayey <br />on-site soils is typically in the range of 10-7 to 10"8 cm/s but the conductivity of in- <br />place interim cover soils (which exhibit otherwise similar characteristics) is on the <br />order of 10"5 to 10-6 cm/s. <br />Though perhaps the most important threat to cover performance, there is no <br />methodology available to describe the degradation process in a way that would be <br />realistic for input into an unsaturated flow analysis. In order to accommodate this <br />difficulty, moisture flux modeling was performed based on material <br />characteristics that are degraded in a fashion similar to that observed at the FSL. <br />That is by degrading the hydraulic conductivity to about 3x10-6 cm/s and using the <br />soil suction data associated with these weathered soils. <br />4.4.1 PRESCRIPTIVE FINAL COVER <br />Modeling of a prescriptive final cover for the FSL was conducted using LEACHM <br />in order to allow for performance comparison to the alternative final cover. It <br />should be noted that since the proposed cover will be constructed to a prescriptive <br />standard and is assumed to weather in response to the same conditions that would <br />affect a prescriptive cover, the soil characteristics in the two model scenarios are <br />the same. As a result, the most significant difference between the two models is <br />the root distribution which is limited to the one -foot vegetative layer in the <br />prescriptive case but extends to a three feet in the alternative case. <br />4.4.1.1 SOIL MOISTURE RESULTS <br />Figure 2 depicts the modeled moisture content of the modeled degraded <br />prescriptive final cover soils in percent by weight for six distinct depth intervals <br />over a period of approximately ten years. As can be seen, in all cases for the <br />constant potential boundary condition the shallow layers (3 -inch, 9 -inch, 15 -inch <br />and 21 -inch) mimic seasonal precipitation patterns throughout the modeling <br />period, while the deeper soil layers reflect only severe precipitation events. 0 <br />-10- <br />CA2003-033\EDOM HILL ALTERNATIVE COVER.DOC\6/16/2005 <br />GeoLogic Associates <br />
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