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ARCHIVED REPORTS_XR0002255
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545204
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ARCHIVED REPORTS_XR0002255
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Last modified
1/27/2020 2:52:27 PM
Creation date
1/27/2020 2:39:35 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002255
RECORD_ID
PR0545204
PE
3528
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
02
SITE_LOCATION
502 E GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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Jonas & Associates Inc <br /> representative of subsurface conditions The vacuum pressure reading on the <br /> purging apparatus was recorded to evaluate soil permeability and provide a better <br /> understanding of sod vapor readings The samples were collected through a septum <br /> ' located immediately adjacent to the probe on the sampling apparatus Each sample <br /> was collected with a microsyringe and injected into a gas chromatograph for analysis <br /> (EA, 1987) <br /> Points were chosen on the four sides of the tank area toP ermit estimation of the <br /> ' directional migration, if any, of gasoline vapors In the course of the sampling day, <br /> four standards and three system blanks were run (EA, 1987) <br /> 22 Soil Investigation <br /> During two subsurface investigations performed from 1986 to 1988, soil samples <br /> were collected during the drilling of eight soil borings (see Figure 3-1) at <br /> ' <br /> approximately 5-foot intervals using a 2 5-inch inside diameters litspoon sampler <br /> containing three brass tube liners The sampler was driven 18 inches beyond the <br /> ' tip of the auger by a 140-pound hammer dropping 30 inches The number of blows <br /> was counted for each 6-inch interval the sampler was advanced The brass sample <br /> tubes were then quickly extracted from the sampler The ends of the samplers in <br /> the two brass tubes closest to the shoe of the sampler were examined by a geologist <br /> and logged according to the Unified Soil Classification System prior to being labeled, <br /> capped, sealed and placed on ice The soil collected in the brass tube farthest from <br /> ' the shoe was logged, placed in a glass airtight container, and held for headspace <br /> analysis To avoid cross contamination, the sampling equipment was cleaned with <br /> potable water and trisodium phosphate prior to collecting each sample <br /> After heating the glass sample containers until warm, headspace vapors were <br /> analyzed with a Thermoenvironmental 580A Organic Vapor Analyzer (OVA) The <br /> OVA was periodically calibrated to measure all of the ionizable hydrocarbons as if <br /> they were benzene, using a standard gas The results of these field analyses were <br /> noted on the drilling logs (Appendix C), and were used to select soil samples <br /> appropriate for laboratory analysis <br /> Two to four soil samples were selected from each boring for laboratory analysis, <br /> ' according to the following criteria <br /> (1) The sample collected closest to the encountered water table <br /> 1 (2) The sample collected five feet below the encountered water table <br /> (3) The sample with the highest apparent hydrocarbon concentration <br /> (4) The deepest sample with apparent presence of hydrocarbons <br /> 3 <br /> 1 <br />
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