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2900 - Site Mitigation Program
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PR0523598
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Last modified
5/20/2020 11:05:11 AM
Creation date
5/20/2020 10:03:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0523598
PE
2960
FACILITY_ID
FA0015928
FACILITY_NAME
TAOC 6TH ST TRACY RAILYARD (BOWTIE)
STREET_NUMBER
11
Direction
W
STREET_NAME
SIXTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
23515016
CURRENT_STATUS
01
SITE_LOCATION
11 W SIXTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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Lee Higgins - 7 - 7 December 2010 <br /> Chevron, TAOC Tracy Rail Yard <br /> concentrations detected in the sample from TRY-29 at a depth of five feet bgs, are <br /> inconsistent with the low TPHc detection of 240 mg/kg TPHc. AMEC concluded the elevated <br /> PAHs detected are unrelated to the historical crude oil pipelines, likely originating from another <br /> source. The PAH findings will be addressed by UPRR's consultant and incorporated into a <br /> health risk assessment report to be submitted to the DTSC for review. <br /> According to the Report, and similar to soil conditions at OU-2, TPH affected soil present at <br /> depths greater than 11 feet bgs extending to approximately 20 feet bgs, was encountered <br /> along the central-western edge of OU-5. The area of affected soil is adjacent to and about <br /> 100 to 200 feet to the north of, the historical TAOC pipelines. The lateral extent of affected <br /> soil has been defined at about 200 feet north-northeast of the former TAOC pipeline <br /> alignment. The vertical extent of affected soil was defined by analytical results of ND for TPHc <br /> for samples collected at a depth of approximately 21 feet bgs, and where visually affected soil <br /> was not observed in drill cuttings. <br /> However, the lateral offsite extent of TPH affected soil/groundwater offsite to the west and <br /> south of OU-5 into adjacent residential areas has not been adequately delineated, and will be <br /> addressed by future offsite soil and groundwater investigations. <br /> Groundwater <br /> TPHd was detected in six of the 13 samples submitted for analysis, with concentrations <br /> ranging from 68 to 510 fag/L. BTEX were not detected. PAHs were detected in 10 samples, <br /> and four carcinogenic PAHs detected had TEQs ranging from 0.0043 to 0.022 pg/L. Analytical <br /> results of the four downgradient boring samples for TPHd were ND at the MDL of 100 pg/L. <br /> Evaluation of the TRY-29 groundwater sample chromatogram determined that the TPHd <br /> present (5,600 pg/L) is consistent with severely biodegraded San Joaquin Valley crude oil and <br /> possibly bunker fuel. <br /> Soil Vapor Sampling <br /> One offset location (SV-E) near prior borings with elevated TPH in soil and groundwater in <br /> close proximity to adjacent residential areas, was chosen for collecting soil vapor samples at <br /> depths of five and ten feet bgs. Vapor samples were submitted for analysis of BTEX and <br /> naphthalene. Similar to results in OU-2, 3, and 4, benzene and naphthalene were ND in all <br /> samples at respective laboratory reporting limits. However, low concentrations of toluene, <br /> ethylbenzene, and xylenes were detected. The analytes detected did not exceed their <br /> respective residential or commercial environmental screening levels. <br /> According to AMEC's Report: <br /> • Analytical results of soil vapor samples collected from five impacted areas bordering <br /> adjacent residential areas, did not detect benzene or naphthalene above environmental <br /> screening levels. Low concentrations of toluene, ethylbenzene, and xylenes did not <br /> exceed respective method detection limits. AMEC summarized that the data indicates <br /> the soil vapor at those locations is not significantly impacted. <br />
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