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2900 - Site Mitigation Program
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PR0542420
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/23/2020 9:31:51 AM
Creation date
1/23/2020 9:24:33 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0542420
PE
2960
FACILITY_ID
FA0024376
FACILITY_NAME
FORMER CHEVRON 98632
STREET_NUMBER
575
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
575 W GRANT LINE RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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CONESTO3A-ROVERS <br /> & ASSOCIATES <br /> January 6, 2011 6 Reference No. 632277 <br /> • TPHg by EPA Method TO-3 <br /> • BTEX and MTBE by EPA Method TO-15 <br /> • Oxygen, Carbon Dioxide, and Helium by American Society for Testing and Materials <br /> (ASTM) Modified Method D-1946 <br /> The results of the current and previous sampling events are presented in Table 1. Copies of the <br /> soil vapor sample laboratory analytical reports and COC documentation are included as <br /> Attachment E. The current results are discussed below. The duplicate sample analytical results <br /> are not included in the following discussion, as similar concentrations within an acceptable <br /> range were detected in both samples. Please refer to Attachment E for the duplicate sample <br /> analytical results. <br /> Table 1 also presents a comparison with the San Francisco Bay Regional Water Quality Control <br /> Board (RWQCB) ESLs for shallow soil gas at commercial or industrial sites. The ESLs are for <br /> use as screening levels in determining if further evaluation is warranted, in prioritizing areas of <br /> concern, in establishing cleanup goals, and in estimation of potential health risks. As stated by <br /> the RWQCB, the ESLs are considered to be conservative. The presence of a chemical at a <br /> concentration above an ESL does not necessarily indicate that adverse impacts to human health <br /> or the environment are occurring; exceeding ESLs indicates that the potential for impacts may <br /> exist and that additional evaluation may be needed. <br /> Discussion of Results <br /> TPHg-was-detected in VP-1,ALP-2,andYR-3atconeentrations_nf100,0o0,o0Dilg/m3" <br /> 66,000 µg/m3, and 14,000 µg/m3, respectively. The concentrations in VP-1 and VP-2 <br /> exceeded the commercial/ industrial ESL of 29,000 µg/m3. <br /> • Benzene and ethylbenzene were only detected in VP-1 (26,000 µg/m3 and 6,600 ltg/m3, <br /> respectively) and VP-2 (6.3 µg/m3 and 10 µg/m3, respectively) . The concentrations in VP-1 <br /> exceeded the commercial/ industrial ESLs of 280 µg/m3 and 3,300 µg/m3, respectively. <br /> • Xylenes were only detected in VP-1 (3,200 µg/m3) . The detected concentration was well <br /> below the commercial/industrial ESL of 58,000 µg/m3. <br /> • No toluene or MTBE was detected. <br /> • Similar TPHg and benzene concentrations were detected in VP-1 relative to the <br /> October 2009 event, while the toluene and MTBE concentrations decreased (not detected) . <br /> Ethylbenzene and xylenes were not detected in VP-1 during the previous event, but the <br /> reporting limits were elevated. <br /> • In VP-2 and VP-3, higher TPHg concentrations were detected relative to the October 2009 <br /> event. No significant changes in concentration were reported for the other constituents. <br /> Worldwide Engineering, Environmental, Construction, and IT Services <br />
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