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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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EHD - Public
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Mr Jeff Baker <br /> 2 <br /> Stockton Terminals Technical`nmittee 10 July 2009 <br /> • <br /> COC concentrations generally occurred in A zone wells on the BP property. The highest <br /> concentrations of TPHg and TPHd were in AR/MW-3A and AR/MW-10A at <br /> 64,000 micrograms per liter (pg/L) and 220,000 pg/L, respectively. The highest <br /> concentrations of benzene and TBA were detected in B zone monitoring well <br /> AR/MW-8B at 11,.000 and 5,000 pg/L, respectively. The highest concentration of MTBE <br /> was observed in AR/MW-50 at 22,000 pg/L. However, the 9,000 pg/L of MTBE <br /> observed in AR/MW-8A represents a trend of increasing concentrations that started at <br /> about 20 pg/L in 2001. <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 /> (lbs/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 wells, two midpoint <br /> wells, and four trigger wells. Between January and March 2009, the STTC estimates <br /> that the east system and west system had run times of 61 and 59 percent, respectively. <br /> The STTC attributes the excessive east system down-time to maintenance-related <br /> power interruptions. The west system down-time was attributed to excessive rainfall. <br /> The STTC estimates that collectively, 315 pounds of ozone were injected and <br /> 105 pounds of hydrocarbons were destroyed during this period. Ozone production <br /> equipment was upgraded during the first quarter of 2009 with the objective of increasing <br /> system run times. <br /> The STTC monitors the ozone injection system using 12 A- and B-zone wells. A <br /> contingency plan is triggered if the concentrations of BTEX, MTBE or TBA in any <br /> remedial observation wells exceed compliance limits. Table 12 shows that the TBA <br /> concentrations in remedial observation well AR/MW-18B over the last two quarters <br /> have been 13 and 31 pg/L. These two consecutive concentrations exceed the <br /> compliance limit of 6.6 pg/L. Pursuant to the terms described on Page 3 of the Revised <br /> Contingency Plan (Appendix K of the First QMR), three consecutive exceedences of an <br /> order of magnitude greater than the compliance limit trigger installation of a second <br /> ozone sparge array east of the remedial observation wells. <br /> Our comment is presented below. <br /> 1. The trend of increasing MTBE concentrations observed in AR/MW-8A shows that <br /> this compound is migrating southeast from AR/MW-50. However, there are no wells <br /> between the AR/MW-8A and the West OS system, located about 400 feet <br /> downgradient, to delineate and track the downgradient migration of MTBE and other <br /> petroleum hydrocarbons on to the property to the southeast. In the Second QMR <br /> due on 1 August 2009, please discuss any potential sources for this increasing <br /> concentration trend and provide any insight on whether mitigative measures are <br /> necessary. <br />
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