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SITE INFORMATION AND CORRESPONDENCE_2001-2018
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_2001-2018
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Last modified
4/9/2020 8:57:17 AM
Creation date
3/30/2020 1:29:30 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2001-2018
RECORD_ID
PR0009241
PE
2960
FACILITY_ID
FA0004015
FACILITY_NAME
SHELL OIL (STOCKTON PLANT)
STREET_NUMBER
3515
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16203002
CURRENT_STATUS
01
SITE_LOCATION
3515 NAVY DR
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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/ Mr. Jeff Goold - 3 - 10 October 2008 <br /> Shell Stockton Terminal • • <br /> t <br /> The Pilot Test Report presents the results of DPE pilot testing conducted between <br /> 12 and 16 May 2008. DPE extraction was conducted from three newly installed extraction <br /> wells, including MW-37 in the MW-1 hot spot, MW-38 in the MW-13R hot spot, and MW-39 in <br /> the MW-10 hot spot. The extraction wells were installed to total depths ranging between <br /> 26 and 30 feet bgs. Observation wells P-1 and P-2 were installed in the MW-1 and MW-10 hot <br /> spots, respectively. Soil samples were collected for laboratory analysis from the five well <br /> borings. Results showed that the concentrations in soil samples from all borings were <br /> generally low to ND for BTEX and oxygenates. Maximum concentrations of TPHg and TPHd <br /> were in P-1 at 660 mg/kg and 180 mg/kg, respectively. <br /> During the DPE pilot test, the groundwater level was lowered in each extraction well using a <br /> pneumatic pump at rates that averaged about two gallons per minute (gpm) from MW-37, <br /> three gpm from MW-38, and one gpm from MW-39. Maximum petroleum hydrocarbon <br /> concentrations were present in groundwater extracted from MW-37. TPHg was detected at <br /> 2,000 pg/L, benzene at 110 pg/L, MTBE at 100 pg/L and TBA at 2,700 pg/L. The extraction <br /> test was repeated in MW-37 using a submersible electric pump to evaluate the maximum <br /> groundwater extraction rate. Groundwater extraction averaged about three gpm during this <br /> phase of the DPE pilot test, and about two feet of drawdown was observed in a monitoring <br /> well located about 18 feet from extraction well MW-37. <br /> Vapor phase extraction was performed in stepped rates consisting of two two-hour steps and <br /> one seven-hour step. Sustained applied vacuums varied between 17 inches of mercury (in Hg) <br /> to 24 in Hg. A maximum sustained flow rate of 48 standard cubic feet per minute (scfm) was <br /> attained from MW-38. Maximum vapor concentrations were obtained from MW-37 during the <br /> extra extraction event at a flow rate of 32 scfm. At this flow rate, TPHg was detected at ' <br /> 24,000 parts per million by volume (ppmv). BTEX was detected at 220, 57, 70, and 185 ppmv, <br /> respectively, and MTBE was detected at 28 ppmv. <br /> By observing a pressure response that was about 3% of the applied vacuum in a well located <br /> about 11 feet from extraction well MW-39, Shell calculated that a radius of influence (ROI) of <br /> about 12 feet could be used as a design basis for all three hot spots. Shell recommends <br /> implementing DPE to remediate the three hot spots and is prepared to submit a Remedial <br /> Action Plan (RAP) within 60 days of approval of the Pilot Test Report. <br /> Our comments are presented below. <br /> 1. Except for the detection of 150 mg/kg of TPHg in the MW-39 borehole, the results of the <br /> Investigation Report show that petroleum contamination in vadose zone soils has been <br /> delineated. The laboratory analytical results for groundwater samples obtained from off-site <br /> borings SB-25 to SB-26 show that the leading edge of the plume also has been delineated <br /> to ND. The grab groundwater samples from hot spot borings SB-22 through SB-24 all' <br /> detected petroleum hydrocarbons exceeding their respective WQOs in groundwater <br /> beneath the continuous sand unit present between 70 and 80 feet bgs. Therefore, the <br /> installation of monitoring wells screened below the continuous sand unit is necessary to <br /> monitor potential plume migration and the progress of site cleanup. <br /> 2. We do not concur that the ND results reported in the Soil Vapor Report for the outdoor <br /> ambient air samples provide any data useful for evaluating potential indoor air intrusion <br /> from the elevated petroleum hydrocarbons concentrations in soil vapor. Flowing outddor air <br />
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