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ARCHIVED REPORTS_XR0007692
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0507153
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ARCHIVED REPORTS_XR0007692
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Last modified
10/8/2020 10:41:12 PM
Creation date
6/23/2020 10:21:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007692
RECORD_ID
PR0507153
PE
2950
FACILITY_ID
FA0007717
FACILITY_NAME
THRIFTY OIL #171
STREET_NUMBER
1250
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
11731001
CURRENT_STATUS
02
SITE_LOCATION
1250 N WILSON WAY
QC Status
Approved
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LSauers
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EHD - Public
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' GeoHydrologic Consultants, Inc <br /> GHC recommends performing vapor extraction combined with groundwater extraction <br /> ' (by pumping) and treatment (MPE) as the preferred remedial solution for the shallow <br /> zone, with groundwater extraction only recommended for the deeper zone well (EW-513) <br /> The downhole pumps will not only extract the impacted groundwater for treatment but <br /> ' will also lower the water table thus exposing more soil to vapor extraction We believe <br /> that this technology will achieve the same remedial goals more quickly than dual-phase <br /> extraction and at a lower overall cost since this type of system has a significantly higher <br /> ' "up time" and once the vapor goals are reached beneath the Site the vapor extraction <br /> system can be shut down while the groundwater extraction portion of the system <br /> continues to capture and cleanup the groundwater plume, if needed <br /> Based on the multi-phase extraction pilot tests (average ROI approximately g pp ately 30 to 50 <br /> feet), GHC recommends using existing groundwater monitoring wells TB-3, TB-4, TB-6, <br /> TB-7, TB-10, MW-2, extraction well EW-5S, and vapor well VW-5 for conducting vapor <br /> extraction activities while simultaneously extracting groundwater from the six wells <br /> including TB-7, TB-10, MW-2, MW-4, EW-5D, and EW-5S (Figure 10) Since <br /> ' moderate to high concentrations of soil vapors were extracted during the most recent pilot <br /> tests which mostly consisted of TPHg in the vapor and dissolved phase, GHC <br /> recommends these remedial activities be performed with a fixed permanent vapor <br /> ' extraction and thermal/catalytic oxidation system, since these pilot test results are <br /> indicative of a moderate to large mass of hydrocarbons in the subsurface The strategy of <br /> remediation will be to concentrate contaminant removal efforts in the area of greatest <br /> contamination surrounding the previous tank cluster <br /> Based on available information, the current onsite Baker Furnace vapor extraction system <br />' consisting of a positive displacement blower capable of moving air at 250 scfm at about <br /> 15-inches of mercury vacuum will be sufficient for vapor extraction at the Site The <br /> treatment technology is currently anticipated to be a thermal/catalytic oxidizer based on <br />' the pilot test results The vapor phase will be treated and discharged under the existing <br /> Site specific permit issued by the APCD Currently wells TB-3, TB-4, TB-6, TB-7, TB- <br /> 10, MW-2, MW-4, and VW-5 are connected to the vapor extraction system, however, <br /> well EW-5s will need to be connected to the existing piping using 2-inch diameter <br /> schedule 40 PVC If this well is tied into an existing vapor extraction line, a valve should <br /> be placed inside the well box so that the newly added wells can be isolated for vapor <br />' sampling purposes if needed <br /> Groundwater will be extracted using downhole pneumatic pumps (six QED Hammerhead <br /> Pumps) powered by an above ground air compressor(15 cfm Ingersol Rand Continuous <br /> Duty Two Stage Air Compressor) Extracted groundwater is expected to be a combined <br /> flow rate of five to ten gpm The extracted liquids will be pumped into a 500-gallon <br />' settling tank and then the liquid stream will be routed through two 1,000-pound granular <br /> activated carbon vessels and a flow meter/totalizer before permitted discharge to the <br /> sanitary sewer This equipment should be able to be accommodated in the existing 15 <br />' foot by 20 foot remediation compound that already contains a secondary containment <br /> berm <br /> TOC 171 Pilot Study <br /> Page 25 <br />
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