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ARCHIVED REPORTS XR0001794
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544475
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ARCHIVED REPORTS XR0001794
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Last modified
5/17/2019 3:41:53 PM
Creation date
5/17/2019 3:30:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001794
RECORD_ID
PR0544475
PE
3528
FACILITY_ID
FA0003602
FACILITY_NAME
TESORO (SHELL) 68151
STREET_NUMBER
35
Direction
N
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04318003
CURRENT_STATUS
02
SITE_LOCATION
35 N CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Station No. 502, 35 N. Cherokee Lane, Lodi , - Interim Remediation Plan <br /> The influent level at the conclusion of the initial phase of remediation <br /> was less than 3,000 ppm. Consequently, the above process and emission <br /> rates are higher than what we actually expect to encounter. <br /> Deactivation <br /> When soil vapor levels have been reduced to an acceptable level , the <br /> system will be given a final monitoring and then deactivated. The above <br /> ground components of the system including the catalytic incinerator, the <br /> pump, accumulator, fence and propane trap wagon, will be removed from the <br /> site. The underground piping and manifold will remain in place and could <br /> be used for any potential future remediation, if necessary. <br /> PROJECT MANAGEMENT AND REPORTING <br /> Project Management will coordinate the system monitoring, review the <br /> results, implement compliance control , and submit summary reports to <br /> Ultramar. Project Management will also submit routine reports on the <br /> operation as required by the Air Pollution Control District. The project <br /> management function will be overseen by an EVAX Project Engineer. <br /> PUBLIC HEALTH RISK <br /> A screening level assessment of the public health risk due to the <br /> emission of benzene from the incinerator was undertaken using the ARB <br /> version of the dispersion model PTPLU. The maximum one-hour ground-level <br /> benzene concentration modeled by PTPLU was converted into excess cancer <br /> risk using the procedures outlined in the CAPCOA Air Toxics Assessment <br /> Manual . These procedures are quite conservative in nature and tend to <br /> overstate the actual risk by a large margin. <br /> The maximum benzene emission rates were risk screened using the risk <br /> criteria developed by the San Francisco Bay Area Air Quality Management <br /> District (BAAQMD). The BAAQMD generally considers projects with a cancer <br /> risk between I to 10 cases per million population to be acceptable, <br />' particularly if the operation is short-term and involves a T-BACT <br /> emissions control device. <br /> The risk assessment was based on an analysis of the benzene emissions <br /> since benzene has the highest cancer risk factor of the typical <br /> constituents of gasoline. The ratio of benzene to total hydrocarbons in <br /> this emissions assessment is typical of that found in gasoline. <br /> It was determined that the excess lifetime cancer risk associated with a <br /> benzene emission rate of 0.20 lbs/day was less than 3 cases per million <br /> population based on a continuous 70 year operation. This figure is well <br /> - 8 - <br />
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