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ARCHIVED REPORTS_2013_7
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ARCHIVED REPORTS_2013_7
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Last modified
9/14/2020 4:01:31 AM
Creation date
7/3/2020 11:06:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_7
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_2013_7.tif
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EHD - Public
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groundwater impacts. Measures such as reducing the moisture flux through wastes to limit <br /> leachate and landfill gas generation reduce the potential for related impacts to groundwater. <br /> As discussed in the Phase II EMP (GLA, 2012), groundwater monitoring data suggest that <br /> VOC concentrations do not exceed the respective Maximum Contaminant Levels beyond the <br /> Point of Compliance, and dispersion alone will attenuate VOC concentrations to below <br /> practical quantitation limit concentrations levels within 1000 feet of the landfill. In addition, <br /> currently there are no users of groundwater or environmental receptors within one mile of <br /> the CHSL. These conditions suggest that intrinsic remediation is an effective mitigation <br /> strategy that could be used to manage VOC concentrations. <br /> EMP monitoring wells are located such that they would form the intrinsic remediation <br /> monitoring network (Figure 10). Each well is screened to intercept the shallow aquifer and <br /> are positioned to provide groundwater chemistry information at varying directions and <br /> distances from the landfill (Table 11A). Costs for this alternative are typically associated with <br /> installation, sampling, and maintenance of groundwater monitoring wells. Since three new <br /> offsite monitoring wells were constructed as part of the EMP, there is no capital cost <br /> associated with implementing this alternative aside from installing optional bladder pumps <br /> to facilitate sampling and negotiating this alternative with the regulatory agencies (Table <br /> 11B). Operations and maintenance costs are included on Table 11C, and are those <br /> associated with additional groundwater monitoring and reporting. <br /> 4.5 GROUNDWATER EXTRACTION WITH EX-SITU TREATMENT <br /> Considering the low hydraulic conductivity of the Corcoran Clay aquifer materials at the site <br /> and the low yields that are available from wells, the groundwater extraction and treatment <br /> methods are not likely to pull in contaminated groundwater from the far edges of the plume, <br /> but rather would form a hydraulic barrier that would inhibit future migration of contaminant <br /> groundwater past the point of compliance. <br /> 4.5.1 Systems Common to Both Ex-Situ Treatment Systems <br /> Groundwater Extraction System. Both of the ex-situ treatment systems that are considered <br /> herein have a common groundwater extraction system that is configured to contain VOC- <br /> impacted groundwater along the point of compliance between wells MW-8 and SB-1 (Figure <br /> 11). Pumped groundwater will be conveyed to an above-ground treatment system that is <br /> unique to each of the two remedial alternatives. Based on recent limited aquifer tests, it is <br /> assumed that the groundwater extraction wells will be positioned approximately 100-feet <br /> Engineering Feasibility Study Geo-I.og0c Page ■ 25 <br /> Corral Hollow Sanitary landfill ASSOCIATES <br /> January 25,2013 <br />
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