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SITE INFORMATION AND CORRESPONDENCE_FILE 2
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0503286
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SITE INFORMATION AND CORRESPONDENCE_FILE 2
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Last modified
1/17/2020 4:46:54 PM
Creation date
1/17/2020 2:20:17 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 2
RECORD_ID
PR0503286
PE
2953
FACILITY_ID
FA0005766
FACILITY_NAME
MOBIL OIL BULK PLANT
STREET_NUMBER
500
Direction
E
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25027008
CURRENT_STATUS
01
SITE_LOCATION
500 E GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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KEY ISSUES <br /> FORMER MOBIL OIL BULK PLANT <br /> 500 East Grantline Road <br /> Tracy, California <br /> January, 1994 <br /> ■ No liquid- or separate-phase hydrocarbons have been observed or encountered in the <br /> groundwater at any time during soil excavation/remediation activities and throughout <br /> the groundwater monitoring program to this date. Soil was excavated to below the <br /> groundwater and no separate-phase product was observed in the groundwater at any <br /> time, even as sheen. <br /> ■ Petroleum hydrocarbons detected in the capillary fringe or zone are addressed as part <br /> of the dissolved-phase hydrocarbon plume in the groundwater. <br /> ■ Grab water sample from Boring B-7 is not considered an accurate representative of the <br /> water-bearing zone. This sampling technique is used for screening purposes only since <br /> the procedure is not consistent with standard sampling protocol for properly constructed <br /> monitoring wells. In some instances, the grab water sample can be spiked with the <br /> overlying contaminated soil, if present, such that the analytical result is higher than for <br /> a similar sample collected from a properly constructed and developed well. Analysis of <br /> groundwater samples collected from the confirmation monitoring well AW-9 installed <br /> adjacent to Boring B-7 did indeed reveal lower hydrocarbon concentration and in some <br /> instances, no detectable levels of hydrocarbon constituents. While several regulatory <br /> agencies have allowed the use of this qualitative survey method as a cost-effective <br /> measure to assist in the investigation of hydrocarbon plumes, it still does not provide a <br /> quantitative representation of actual field conditions. <br /> ■ Residual petroleum hydrocarbons remaining beneath the site,if any, are primarily in the <br /> capillary zone of the upper water-bearing unit and in the groundwater. <br /> ■ Adsorbed-phase petroleum hydrocarbons in the vadose (unsaturated) zone beneath the <br /> site have been adequately defined and effectively removed and remediated. <br /> ■ The extent of dissolved-phase hydrocarbon plume in the groundwater has been <br /> adequately defined both onsite and offsite. Historical monitoring and sampling data <br /> indicate a generally decreasing trend of the hydrocarbon concentration in the <br /> groundwater over time. <br /> ■ Benzene was detected only in one of the samples collected from the S onsite wells in <br /> October 1993 at a concentration of 0.76 parts per billion. During this sampling event, <br /> total petroleum hydrocarbons (TPH) were not detected in any of the water samples, <br /> except for TPH as diesel in two of the onsite wells at a concentration of up to 190 ppb. <br /> ■ The linear velocity of groundwater represents advective flow and the mass movement <br /> of groundwater through the media. Contaminant transport/migration, however, is <br /> influenced by other factors,such as sorption,biodegradation,and volatilization. The rate <br /> of contaminant transport is lower than the advective movement of groundwater. <br />
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