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EHD Program Facility Records by Street Name
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2200 - Hazardous Waste Program
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PR0505941
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Last modified
12/17/2024 2:39:30 PM
Creation date
4/5/2019 8:21:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0505941
PE
2220
FACILITY_ID
FA0006033
FACILITY_NAME
PG&E: Tracy Service Center
STREET_NUMBER
502
Direction
E
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
250-020-05
CURRENT_STATUS
01
SITE_LOCATION
502 E GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\HW\HW_2220_PR0505941_502 E GRANT LINE_.tif
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EHD - Public
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I <br />plastic bag, examined visually for gas plant residues, and held for <br />headspace analysis. In the event of poor sample recovery, the lead tube <br />will be retained for possible analysis, and the remaining recovered soil <br />will be examined as above. <br />Visual and olfactory observations noted during the previous investigation at <br />the Tracy site (PG&E 1987) suggest that gas plant residues exist in soil to <br />a depth of approximately 5 feet in those areas investigated. It is <br />therefore anticipated that soil borings will be typically advanced to a <br />depth of 10 feet. <br />' Drilling augers will be steam cleaned between each boring to minimize the <br />potential for cross -contamination. Runoff from steam -cleaning operations <br />will be contained and stored for appropriate disposal. <br />3542a/BAV102 9 <br />The initial determination of the presence of gas plant residues in soil <br />for laboratory <br />borings, and the selection of soil samples analysis, will be <br />based on a qualitative screening process performed in the field. After <br />' <br />heating each soil sample bagged for field analysis, headspace vapors will be <br />analyzed with a Photovac TIP 1 Air Analyzer (PID). The PID will be <br />calibrated several times each day, using a gas containing known hydrocarbon <br />concentrations. The resulting data will provide a qualitative measure of <br />the presence of ionizable hydrocarbons in soil samples. This information, <br />along with visual and olfactory observations, will provide the basis for <br />soil sample selection for laboratory analysis. <br />The depth of each boring will be determined by the extent of any gas plant <br />residues encountered in the field. At those locations where residues are <br />encountered, soil borings will be advanced to a depth two sample intervals <br />below the deepest apparent residues detected in the field, to a maximum <br />depth within 5 feet of the bottom of the uppermost aquifer (estimated at <br />approximately 50 feet below the ground surface). At those locations where <br />no gas plant residues are detected in the field, borings will be advanced to <br />' <br />a maximum depth of 10 feet. Section 4.2.1.3 provides the soil sampling <br />interval rationale for this investigation. <br />Visual and olfactory observations noted during the previous investigation at <br />the Tracy site (PG&E 1987) suggest that gas plant residues exist in soil to <br />a depth of approximately 5 feet in those areas investigated. It is <br />therefore anticipated that soil borings will be typically advanced to a <br />depth of 10 feet. <br />' Drilling augers will be steam cleaned between each boring to minimize the <br />potential for cross -contamination. Runoff from steam -cleaning operations <br />will be contained and stored for appropriate disposal. <br />3542a/BAV102 9 <br />
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