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ARCHIVED REPORTS_2009_24
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ARCHIVED REPORTS_2009_24
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Last modified
7/17/2020 9:01:35 PM
Creation date
7/3/2020 10:55:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2009_24
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_2009_24.tif
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EHD - Public
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6.5 DRAIN GAUGE LYSIMETERS <br /> Two Drain Gauge lysimeters were installed at each monitoring location as illustrated on Figure <br /> 2. These instruments have measured no infiltration to date at any location. This indicates that <br /> while the soil may wet during the winter, breakthrough (infiltration into the waste) has not <br /> occurred. <br /> 7.0 MODELING RESULTS <br /> Climatic data collected from the MET station was used to remodel the performance of the 4-foot <br /> thick alternative final cover using a combination of the actual final cover soil properties in the <br /> original design report (GLA, 2004) and the data generated during the soils re-calibration study of <br /> 2007. The original soil characteristics and results of the re-calibration have been used to model <br /> both the soil moisture content and moisture flux, and are summarized in Figures 12 and 13, <br /> respectively. <br /> 7.1 MOISTURE CONTENT <br /> As indicated by a comparison of monitored soil moisture content (Figures 8 and 9)with modeled <br /> soil moisture content (Figure 12), the pattern of moisture content variability resulting from <br /> modeling is generally consistent with the overall moisture trends observed at both the Met and <br /> Satellite stations. That is, both the modeled and monitored data indicate broad seasonal changes <br /> in moisture content with discrete soil moisture responses to individual rain events only being <br /> recorded and anticipated for the most severe events. In addition, the general tendency for deeper <br /> soils to exhibit higher moisture contents is also reflected in both the observed and modeled data. <br /> Two relatively minor discrepancies exist between the modeled and monitored data. First, <br /> individual severe rain events are observed to have a more immediate and dramatic impact on soil <br /> moisture contents than is indicated by modeling. Second, the observed late summer increase in <br /> moisture content is not reflected in the modeling data because LEACHM accounts for only liquid <br /> phase moisture migration. Both of these discrepancies should result in conservatism in the <br /> model results since, 1)the slower soil moisture response modeled allows more time for <br /> infiltration and 2)the introduction of vapor phase (or oxidation created water)would result in <br /> extraction of more water from the soil than is calculated. <br /> 7.2 MOISTURE FLUX <br /> As indicated in Section 6.5 above, no water migration through the bottom of the cover has been <br /> measured by the on-site lysimeters. In addition, as discussed in Sections 6.3 and 6.4, a consistent <br /> upward moisture and soil suction gradient has been observed within the final cover section over <br /> a majority of the year. These results are consistent with the modeled results (Figure 13)which <br /> indicate a net negative flow of moisture (long-term drying)through the final cover system over <br /> the three year monitoring period. <br /> g <br /> GeoLogic Associates <br />
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