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WORK PLANS_PRE 2019
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3000 – Underground Injection Control Program
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PR0009077
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WORK PLANS_PRE 2019
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Last modified
5/11/2021 3:42:10 PM
Creation date
5/11/2021 1:28:04 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3000 – Underground Injection Control Program
File Section
WORK PLANS
FileName_PostFix
PRE 2019
RECORD_ID
PR0009077
PE
2960
FACILITY_ID
FA0004038
FACILITY_NAME
ARCO BULK FACILITY
STREET_NUMBER
2700
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
2700 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Stantec <br /> Site History and Previous Investigations <br /> BP Stockton Terminal No. 40T <br /> June 17, 2009 <br /> manifolds, and a timer. The East System is capable of delivering 15 scfm of ozone to four or <br /> five OS wells simultaneously through piping connected to each individual OS point. The OS <br /> system piping is equipped with a manifold that will allow for the adjustment of the individual well <br /> injection rates. <br /> The West System, which is located at and in the vicinity of the Tesoro Terminal, began <br /> operation on November 15, 2004. This system is connected to 31 "A" zone OS wells (OS-1 <br /> through OS-31) and 8 "B" zone OS wells (OS-16 through OS-8B). The West System is <br /> constructed with the same specifications as described above for the East System. <br /> BP Stockton Terminal No. 40T Summary <br /> Soil and groundwater investigations, at and in the area of BP Stockton Termianl No. 40T (site), <br /> have been conducted by Woodward-Clyde Consultants, Levine and Fricke, Environmental <br /> Strategies Corporation, Kleinfelder, Hydro-Search, Inc., Harding Lawson Associates (HLA), <br /> Hart Crowser, EMCON, IT Corporation, Stantec, and URS for various site tenants beginning in <br /> 1984. Assessment activities conducted specifically on-site include HLA (1990 and 1991), IT <br /> Corporation (IT), and URS. Quarterly groundwater monitoring has been conducted since 1993 <br /> on selected monitoring wells at the site as part of the overall monitoring program performed for <br /> the STTC. <br /> Groundwater samples have been collected from groundwater monitoring well AR/MW-5A, <br /> located in the area of highest dissolved petroleum hydrocarbon concentration quarterly since <br /> 1993. Benzene concentrations in groundwater samples collected from AR/MW-5A during the <br /> quarterly monitoring program have ranged from 24,000 micrograms per liter (Ng/L) in <br /> September 1993 to 290 pg/L in May 2006. Benzene was detected at a concentration of 720 <br /> pg/L during the fourth quarter 2006 sampling event. <br /> Groundwater samples from AR/MW-5A were first analyzed for methyl tert-butyl ether (MTBE) <br /> during the first quarter sampling event in 1999. MTBE maximum concentrations in <br /> groundwater samples collected during the quarterly monitoring program have ranged from <br /> 290,000 pg/L in November 1999 to 18,000 pg/L in October 2006. <br /> Bioremediation treatability studies were conducted by HLA in 1991. The study included the <br /> evaluation of existing microbial populations capable of degrading petroleum hydrocarbons, <br /> evaluation of soil chemistry factors, evaluation of hydrogen peroxide stability in soil, and <br /> evaluation of nutrient supplements to accelerate the degradation of petroleum hydrocarbons. <br /> The results of this study indicated that with the addition of proper nutrients and oxygen, <br /> biological treatment of impacted soil and groundwater is technically feasible. The results of this <br /> study are included in HLAs, Phase 1 Bioremediation Treatability Studies (HLA, 1991). <br /> EMCON conducted a biodegradation evaluation in 1996. The scope included sampling existing <br /> wells for biodegradation indicator parameters and evaluating data consistent with the Air Force <br /> Center for Environmental Excellence protocols for assessing natural attenuation. The data <br /> showed that the plume was stable and aerobic and anaerobic biodegradation processes were <br /> removing hydrocarbon mass and had the capacity to continue removing mass. Pilot testing for <br /> biodegradation enhancement included subsurface application of oxygen releasing compound <br /> installation and biosparging. The results showed that these processes were effective in <br /> improving dissolved petroleum hydrocarbons in the A- and B-zones, but the lateral influence <br /> 0040T Site History and Previous Investigations.doc 2 <br />
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