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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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y "Moe <br /> Cleo logluI nchgics 11tc. Page 10 <br /> Interim Remedial Action Plan <br /> Project No.723.2 <br /> March 7, 2005 <br /> sections detail the methods to achieve hydraulic control of the on site plume and prevent <br /> further dispersion of the contaminants. <br /> 3.2.1. Extraction Well <br /> A sustained pumping rate of 3 gpm was achieved in well EW-1 during the July 2004 pilot <br /> test. This well demonstrated that the site's soils are conducive to groundwater extraction <br /> technology. If pumping had continued in EW-1 then the drawdown would have produced a <br /> cone of depression further exposing soil to be influenced by vapor extraction. The bottom of <br /> this well is at 54.5 feet bgs. <br /> However, the contamination present in off site, down-gradient well MW-208 indicates that <br /> the aquifer is impacted in its screened level of 76 feet bgs (or approximately 37 feet below <br /> the water table). This well contained 4,020 ug/l TPH-G on October 21, 2004 (see Figures 4A <br /> & 4B for geology, soil and groundwater contamination in well set MW-8/108/208). A sand <br /> unit was identified in on site boring MW-101 at 70- 77 feet bgs and sands were also recorded <br /> at this depth in MW-208. The sands may be acting as a preferential pathway for contaminant <br /> transport to the northeast of the site. The bottom of EW-1 is 15 feet higher than this level <br /> and an additional groundwater extraction well is needed because no on site well intercepts <br /> this interval. <br /> GTI recommends installing one additional well, EW-2, to extract groundwater from the sand <br /> units in question. The proposed well EW-2 is shown on Figure 5: Cross Section C —C'. <br /> 3.2.1.1 Soil Boring <br /> Figure 2 includes the proposed well boring location. Well EW-2 will be installed adjacent to <br /> the former dispenser island and in proximity to the existing extraction wells to facilitate <br /> plumbing design. <br /> Prior to commencing work, encroachment permits and soil boring/monitoring well permits <br /> will be secured and the SJC/EHD will be notified 48 hours in advance. The subsurface will <br /> .r be cleared of underground utilities by notifying Underground Service Alert. <br /> The borings will be drilled using a 10-inch outside diameter continuous flight hollow stem <br /> auger. The borehole will be advanced to a depth of 77 feet below the ground surface (bgs). <br /> Soil cuttings will be containerized in DOT approved 55-gallon steel drums and held on site <br /> pending disposal. <br /> 3.2.1.2 Soil Sampling <br /> Soil samples will be collected for geological evaluation with continuous logging starting at <br /> 25 feet bgs and then to total depth. This continuous sampling is designed to fill data gaps <br /> resulting from the five foot sampling interval previously used at the site. Historically heaving <br /> sands have been experienced at the site and if encountered they will be bypassed as necessary <br /> without sampling. Boring logs will be developed by a professional geologist under the <br /> supervision of a registered geologist. The logs will be prepared using the U.S.C.S. and field <br /> V <br />
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