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ARCHIVED REPORTS_1995
EnvironmentalHealth
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4400 - Solid Waste Program
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PR0440003
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ARCHIVED REPORTS_1995
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Last modified
7/17/2020 3:53:09 PM
Creation date
7/3/2020 11:04:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
1995
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440003_31130 CORRAL HOLLOW_1995.tif
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EHD - Public
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layer will not be disturbed. The vegetation will be seeded at the beginning of the rainy <br /> season, so no irrigation will be necessary. <br /> 4.1.3 Groundwater Extraction and Treatment <br /> e leachate-impactedoundwater and treatin it to <br /> This alternative Involves extracting th gr g <br /> reduce concentrations of VOCs to acceptable levels before discharging the treated <br /> groundwater. Typical discharge locations include Corral Hollow Creek (with an <br /> appropriate National Pollutant Discharge Elimination System [NPDES] permit), <br /> wastewater treatment facilities, or spray evaporate over the site (with an appropriate <br /> permit from the RWQCB). Several variables affect the feasibility of this alternative, as <br /> described below: <br /> 9 Aquifer characteristics dictate the number and spacing of extraction wells. <br /> Additionally, the aquifer characteristics determine the capacity of the treatment <br /> system required. <br /> 9 Typical treatment technologies used in the removal of VOCs (COCs found at Corral <br /> Hollow Sanitary Landfill) from groundwater are air stripping, granular activated <br /> carbon(GAC)adsorption,and ultraviolet/photo-oxidation. <br /> 9 Discharge requirements affect both the degree of treatment required (whether <br /> secondary treatment or tertiary treatment is required), and the costs associated with <br /> operating the treatment system. <br /> 9 Air emission restrictions may require air abatement devices for groundwater <br /> treatment technologies such as stripping towers. <br /> The local geology and hydrogeology of the site is characterized by two water-bearing <br /> zones; a shallow perched zone within the Corcoran Clay and a deep regional water- <br /> bearing zone approximately 250-300feet beneath the surface. The shallow perched zone <br /> does not appear to be extensive,rather it is confined to the eastern half of the landfill. An <br /> extraction treatment system could be designed to pump groundwater from the shallow <br /> perched zone within the Corcoran Clay layer to the surface for treatment. Given the low <br /> permeability and subsequent low pumping rates associated with the formation, it is <br /> expected that a significant number of extraction wells (possibly 10 to 20) will be required <br /> to provide sufficient flow to attain hydraulic control of the plume(see Figure 3). <br /> Since the chemicals of concern are VOCs (chlorinated hydrocarbons), either an air <br /> stripping tower or GAC adsorption would be suitable technologies to remove the <br /> contaminants. As the concentration of VOCs is relatively low, GAC adsorption will be <br /> more economical. <br /> SACNN.\PJ0M39\09390031.9$G-94\*:l Rev.0,420/95 <br /> 0939-003.19 4-3 <br />
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