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WORK PLANS FILE 2
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2900 - Site Mitigation Program
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WORK PLANS FILE 2
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Last modified
7/24/2019 11:41:49 AM
Creation date
7/24/2019 11:34:09 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0544690
PE
3528
FACILITY_ID
FA0005839
FACILITY_NAME
CASTLE AUTOMOTIVE REPAIR INC.
STREET_NUMBER
2315
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12510017
CURRENT_STATUS
02
SITE_LOCATION
2315 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Geological Technics fix. '•� <br /> Page 2 <br /> Additional Site Characterization Work Plan <br /> Project No.724.2 <br /> March 15,2005 <br /> • In September and October 1997 five Strataprobe soil borings (SP-1, SP-4 SP-5, SP-5A & <br /> SP-6) were installed at the site. Groundwater samples collected from these borings <br /> indicated the presence of low to moderate levels of TPH-G to a depth of 60 feet bgs. <br /> • In August 1999, one deep screened monitoring well (MW-101) and one soil boring (SB- <br /> 201) were installed at the site. The purpose of these borings was to define the vertical <br /> extent of the groundwater plume. Soil samples collected by use of the SimulProbea <br /> Maxitool from the soil borings tested positive for BTEX and TPH-G compounds to a <br /> depth of 111 feet. Pore water samples, also collected with the SimulProbe, revealed the <br /> presence of BTEX and TPH-G to a depth of 111 feet bgs. <br /> • An abandoned domestic well located at an adjacent residence was destroyed in <br /> accordance with SJC/EHD directives on April 20, 2001. <br /> • A discretely screened deep well (MW-201) was installed in October 2001. The results of <br /> this endeavor suggested that the contamination extended to a depth of 128 feet below <br /> grade surface (bgs). This depth was the target of a SimulProbe°sampling effort and the <br /> soil sample from this elevation contained detectable TPH-G. <br /> • Seven quarterly monitoring events have been completed since the installation of deep <br /> well MW-201. This well was completed with a screened interval of 148 — 150.5 feet bgs. <br /> The amount of contamination in this well has attenuated to trace levels suggesting that it <br /> was a drilling artifact. <br /> • On November 20 — 26, 2003, GTI supervised the installation of three continuous multi- <br /> chambered tubing (CMTTM) wells (MW-7, MW-8 and MW-9, respectively). Each <br /> CMTTM well was constructed with three discretely screened intervals with the bottom cap <br /> comprising an integral 'fourth screen at the terminal depth. The MW-7 CMTTM well <br /> borehole was installed across E. Castle Street approximately 120 feet northwest of the <br /> location of the former dispenser island. The MW-8 CMTTM well borehole was placed <br /> across N. El Dorado approximately 140 feet east of the location of the former dispenser <br /> island in the predominant down gradient groundwater direction. The MW-9 CMTTM well <br /> borehole was placed in an up gradient location on W. Adams Street approximately 220 <br /> feet from the former dispenser island. <br /> • In our September 8, 2003 work plan, GTI proposed a pilot test to evaluate the use of dual <br /> phase extraction technology to clean up the soil and groundwater plumes. Dual phase <br /> extraction involves the use of both soil vapor extraction and groundwater extraction <br /> technologies simultaneously from one well. Extracting groundwater induces a cone of <br /> depression that exposes more impacted soil to vapor extraction. The SJC/EHD approved <br /> the work plan in their November 15, 2003 letter correspondence. Three new extraction <br /> wells (EW-1, VEW-1 and VEW-2) were installed at the site on July 7, 2004 and the pilot <br /> was performed on July 26—31, 2004. <br /> • The results of the dual phase extraction pilot test were detailed in GTI's November 5, <br /> 2004"Dual Phase Pilot Test"report and submitted to the SJC/EHD. <br />
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