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PR0009171
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
3/30/2020 11:50:21 AM
Creation date
3/30/2020 11:19:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009171
PE
2960
FACILITY_ID
FA0004011
FACILITY_NAME
PORT OF STOCKTON-FUEL TERMINAL
STREET_NUMBER
0
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95203
CURRENT_STATUS
01
SITE_LOCATION
NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Mr. Jeff Baker -2 - 20 August 2009 <br /> Stockton Terminals Technicommittee <br /> Since 20 September 2002, the STTC has utilized SoakeaseTM separate phase <br /> hydrocarbon (SPH) removal socks in four wells to remove SPH. The Second QMR <br /> reports that SPH or SPH sheen has recently been observed in only one of these four <br /> wells (TS-4) and in the newly installed TS-RW1. Therefore, the Soakease socks were <br /> transferred to these two wells. Consistent with historical observations, no B, C, or D <br /> zone wells contained SPH. <br /> As shown in Tables 6 and 7, during the second quarter 2009 the highest COC <br /> concentrations generally occurred in A zone wells in the BP aboveground tank (AGT) <br /> area. The highest concentrations of TPHg and TPHd were in AR/MW-8A and <br /> AR/MW-23A, respectively, at 110,000 micrograms per liter (Ng/L) each. The highest <br /> concentrations of MTBE and TBA were detected in AR/MW-50 at 10,000 pg/L <br /> and,2,500 pg/L, respectively. The highest concentration of benzene was detected in <br /> AR/MW-8A at 96,000 pg/L. The MTBE concentration in AR/MW-8A, which has been <br /> steadily increasing since 2001, was detected at 6,600 pg/L during the second quarter. <br /> This concentration is slightly lower than the previous quarter. <br /> Table 6 also includes the results of groundwater sampling, conducted in May, for <br /> methylene blue active substances (MBAS), a surfactant in fire suppression foam. <br /> Central Valley Water Board staff requested that BP conduct sampling for this parameter <br /> to assist in evaluating the effects of a November 2008 fire suppression foam release. <br /> During the first quarter 2009, samples were collected without purging AR/MW-5A, <br /> AR/MW-5C, AR/MW-13C, and AR/MW-14B in the AGT area. BP attributes historically <br /> high petroleum hydrocarbon levels in some Site wells to the fire suppression foam <br /> release. <br /> During the second quarter, BP conducted MBAS sampling in 29 wells in the A through <br /> C zones. Second quarter laboratory analytical results showed that MBAS was detected <br /> at concentrations ranging from 100 pg/L to 2,200 pg/L in these wells. The water quality <br /> objective for MBAS is 500 pg/L. To address the concentrations, BP over-purged up to <br /> 10 well casing volumes from select wells with MBAS. The field data sheets in <br /> Appendix D show that 10 wells were sampled after over-purging, including two of the <br /> wells sampled during the first quarter (AR/MW-5A and AR/MW-13C). The results in <br /> these two wells show that the MBAS concentrations decreased from the first to second <br /> quarter by about 10-fold in AR/MW-5A and by about half in AR/MW-13C. BP <br /> recommends during the third quarter to over-purge the nine wells that contain MBAS <br /> concentrations above 500 pg/L during the second quarter. Purge water is hauled offsite <br /> for treatment and disposal. <br /> In the fall of 2004, the STTC began operation of two ozone sparge (OS) systems to <br /> clean up groundwater pollution migrating downgradient from the Site. The system is <br /> comprised of 57 A zone and 16 B zone wells connected to two 5 pounds-per-day <br /> (Ibs/day) ozone generators. The OS system is divided into two portions. The west <br /> system is downgradient of Tesoro, and the east system is downgradient of BP. System <br /> performance is evaluated using an array of six remedial observation (RO) wells, two <br /> midpoint wells, and four trigger wells. Between January and March 2009, the STTC <br /> estimates that the east system and west system had run times of 79 and 83 percent, <br /> respectively. These runtimes are about 18 and 24 percent better than the previous <br />
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