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ARCHIVED REPORTS_2014_7
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ARCHIVED REPORTS_2014_7
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Last modified
7/17/2020 3:53:50 PM
Creation date
7/3/2020 10:58:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2014_7
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_2014_7.tif
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EHD - Public
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C <br />3-12 <br />estimates for hydraulic conductivities of sandy silts and very fine to fine sands. The calculated <br />hydraulic conductivities are summarized on Table 7. <br />Aquifer pumping tests completed by Camp Dresser McKee Inc. (1999) and groundwater <br />modeling that was completed for the existing Austin Road Landfill by Herst & <br />Associates/Andrews Environmental Engineering ([HA/AEE], 2001) indicate that the hydraulic <br />conductivity of upper aquifer materials in the area is significantly higher (250 ft/d) than was <br />measured in the slug and bail test results. This higher value is consistent with values listed in <br />the literature (Driscoll, 1986) for medium- to coarse-grained sands and appears to most <br />closely approximate the types of materials encountered within water -bearing zones in <br />monitoring wells at the site. <br />Using the hydraulic conductivity value selected by HA/AEE (250 ft/d), an average groundwater <br />gradient of 0.003 percent, and an estimated effective porosity of 0.25, the calculated average <br />linear groundwater velocity at the site is: <br />v = [(K)(h/I)]/n = [(250 ft/d) (0.003)] / 0.25 = 3 ft/d <br />Where: v = velocity (cm/sec) <br />K = hydraulic conductivity (cm/sec) <br />n = effective porosity <br />h/I = gradient <br />3.7.6 Regional Water Quality <br />The San Joaquin hydrologic basin has experienced overdraft for many years. In the Central <br />San Joaquin Irrigation District, which encompasses Forward Landfill, water levels have <br />dropped approximately 70 feet in the past 30 years. Based on groundwater elevation <br />contours published by the San Joaquin County Flood Control and Water Conservation District, <br />the regional groundwater is now typically 10 to 25 feet below msl and flows to the north- <br />northeast. Declining water levels throughout the Stockton area have induced the eastward <br />movement of poor -quality water from the delta sediments. Migration of these saline waters <br />had already impacted the utility of groundwater as far east as Stockton at the time of a 1981 <br />study by the U.S. Geological Survey (USGS) (San Joaquin County Flood Control and Water <br />Conservation District, 1990). The San Joaquin County Flood Control and Water Conservation <br />District has documented a decline in water quality for the Stockton area due to a general <br />increase in chlorides. <br />The regional water quality in the area around Forward Landfill meets the State's Drinking <br />Water Standard. The water is a calcium-magnesium/bicarbonate water type, with total <br />dissolved solids (TDS) concentrations under 500 mg/I. <br />Forward Landfill SWT Engineering <br />Joint Technical Document - April 2014 <br />z:\projects\allied waste\forward\five year permit rvw 2013\jtd-5 yr pr 2013\text\sec 3_final.doc <br />
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