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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
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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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Statrtec � • <br /> September 15, 2008 <br /> Page 5 of 9 <br /> Reference: Response to RWQCB July 30, 2008 Letter <br /> TBA AS A COMPLIANCE ANALYTE <br /> As mentioned above in the Introduction Section, the second issue relates to RWQCB concerns <br /> regarding TBA and recommendations that it be included in the above-described list of compliance <br /> analytes. Because the objective of the EMP was to monitor the potential off-site migration of the <br /> hydrocarbon plume (by comparisons with pre-OS system historical averages) the compliance <br /> analytes including the highly mobile MTBE are more than adequate. There are several reasons for <br /> not including TBA within the compliance analytes. One important reason is the lack of an adequate <br /> data set. Monitoring and Reporting Program (MRP) 93-807 did not require analyses for fuel <br /> oxygenates. This MRP was replaced by MRP 5-01-819 (effective March 28, 2001), which required <br /> an initial round of fuel oxygenate analyses that were to be discontinued if results were non-detect. <br /> The four remedial observation wells (PS/WC-1S, PS/WC-1M, PS/MW-18, and PS/MW-20) in <br /> existence when MRP 5-01-819 was issued were actually sampled in February 2001, prior to the <br /> effective date. The remaining three remedial observation wells (AR/MW-18B, AR/MW-21A, and <br /> AR/MW-21B) were installed and sampled in fourth quarter 2002. Therefore, only 2 of the 7 <br /> remedial observation wells (PS/MW-18 and PS/WC 1 M) have sufficient data to allow calculation of <br /> representative pre-OS system historical averages. Of the remaining five wells, three have been <br /> analyzed for fuel oxygenates (other MTBE) 2 out of 13 quarters; and two wells have been analyzed <br /> for fuel oxygenates 4 and 5 out of 17 quarters, respectively. Therefore, the historical data sets are <br /> inadequate to provide representative pre-OS sparge system historical averages and are in <br /> compliance with previous MRPs and the current MRP R5-2004-0823. <br /> From a geochemical perspective, TBA is not a primary component of gasoline, such as BTEX, and <br /> is not added to gasoline as a fuel oxygenate, such as MTBE or ethanol. TBA is an incidental <br /> byproduct of the production of MTBE and is only present in some gasolines at trace amounts. <br /> Typically, the manufacturing process for MTBE (variably present at zero to ten percent in gasoline) <br /> results in TBA at a fraction of one percent of the MTBE present. More importantly, the vast bulk of <br /> TBA present in a groundwater plume is the byproduct of incomplete biodegradation of MTBE. <br /> Therefore, adding TBA to the compliance analytes for either the remedial observation wells or the <br /> trigger wells does not achieve the objective of the EMP, to monitor the effectiveness of the OS <br /> barrier arrays. Because TBA is only present in some gasolines and at trace levels (less than a <br /> fraction of one percent of the MTBE present) increases in TBA concentrations in remedial <br /> observation or trigger wells are much more likely to document the accumulation of biodegradation <br /> byproducts of MTBE, than the failure of the barrier array system. Furthermore, MTBE and TBA <br /> were present downgradient from the East System ozone barrier array prior to its installation. Near <br /> remedial observation wells PS/MW-18 (A-zone) and PS/WC-1M (B-zone), MTBE had ranged from <br /> 55 to 120 ug/L and TBA from 11 to 2,700 ug/L prior to installation of the array. Therefore, increases <br /> in TBA in trigger wells further downgradient could be due to the migration of TBA already <br /> downgradient of the arrays or biodegradation of MTBE already downgradient of the arrays, rather <br /> than indicating the OS barrier array are not effective. The quarterly evaluation of existing <br /> compliance analytes as part of the EMP is more than adequate to achieve this objective. <br /> Also, Comment Number 2 of the July 30, 2008 RWQCB letter requested a discussion of historical <br /> and recent TBA data. The RWQCB pointed out that in remedial observation well AR/MW-186, <br /> "...The data trends show that TBA sustained concentration increases over three consecutive <br /> quarters, in excess of the only existing historical data point of <5.0 ug/L, from May 2006 to <br /> lASTTC-Stockton\Reports\Resp to RWQCB July 30,2008\Response to RWQCB July 30,2008 Letter final.doc <br />
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