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2900 - Site Mitigation Program
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PR0508450
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Mr. Maurice Benson* <br /> March 4, 2010 <br /> Page 2 <br /> SWMU 33. The TCE tank, steam cleaner, and cleaning tank were removed prior <br /> to April 1992. Previous soil removal actions at SWMU 20 and SWMU 33 <br /> between 1997 and 1999 included removal of sumps, disposal of 332 cubic yards <br /> of contaminated soil, and in-place abandonment (grouting) of sections of the <br /> IWPL, along with implementing institutional controls to prevent impacts to the <br /> remedy. <br /> The planned demolition of Warehouse 10 in 2007 prompted the U.S. Army Corps <br /> of Engineers to conduct further site remedial investigations to assess the impacts <br /> to construction workers and evaluate soil disposal options. Analytical soil data <br /> from the 2007 investigation showed TCE concentrations up to 260 micrograms <br /> per kilogram, indicating that a persistent source still remained beneath the <br /> foundation. <br /> Further investigation of SWMU 20 was conducted in 2008 by additional CPT <br /> work and with installation of a groundwater monitoring well. CPT fieldwork efforts <br /> helped delineate the lateral and vertical extents of contamination in soil gas and <br /> groundwater, with results showing the highest concentration of 32.8 micrograms <br /> per liter (pg/L) at CP0851. Monitoring well LM193AU-NS was installed in the core <br /> of the groundwater plume beneath the SWMU 20 foundation in March 2009 and <br /> was sampled twice, 1Q09 and 2Q09. TCE concentrations in LM193AU-NS <br /> measured 73.1J+ pg/L and 104 pg/L, respectively, for the two quarters before the <br /> well was destroyed during demolition activities at the Warehouse. <br /> SVE Design <br /> The design specifies nine vapor extraction wells and five vapor monitoring well <br /> locations. The VEs are to be installed using pneumatic fracturing techniques to <br /> enhance preferential pathways in unsaturated soil, thus aiding mass removal. <br /> Extraction wells are to be constructed with a 4-inch diameter schedule 40 <br /> polyvinyl chloride (PVC) casing with a planned radius of influence of 40-feet (ft). <br /> Vapor extraction wells will be screened from 6 ft below ground surface (bgs) to <br /> 16 ft bgs. Two vapor monitoring points will be installed at each monitoring well <br /> with 6-inch screens planned at seven (7) and fifteen (15) ft bgs. Vapor <br /> monitoring wells will be located approximately 30-80 ft from the associated <br /> extraction wells. Based on pilot study results from 1999, SVE system's capacity <br /> is inferred to have a maximum flowrate of approximately 350 standard cubic feet <br /> per minute operating at or above 5.5 inches of mercury vacuum. System <br /> operation is anticipated for two years, followed by optimization efforts to meet the <br /> cleanup goal for TCE of 350 parts per billion volume. <br />
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