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ARCHIVED REPORTS_XR0007350
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0545738
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ARCHIVED REPORTS_XR0007350
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Last modified
6/8/2020 12:19:29 PM
Creation date
6/8/2020 11:54:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007350
RECORD_ID
PR0545738
PE
3528
FACILITY_ID
FA0003715
FACILITY_NAME
Tracy Blvd Chevron
STREET_NUMBER
3775
Direction
N
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
3775 N TRACY BLVD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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• FIELD METHODS AND PROCEDURES <br /> Soil Sampling <br /> Exploratory sod borings are drilled by a State-licensed drilling firm Borings are usually <br /> drilled using 8-inch diameter hollow-stem auger drilling equipment Sometimes the <br /> borings will be drilled with smaller diameter solid flight auger equipment The borings <br /> are logged by a Touchstone Developments geologist using the Unified Sod <br /> Classification System and standard geologic techniques The boring logs are <br /> represented in Appendix B Samples are collected by advancing a 2-inch diameter, <br /> split-spoon sampler with brass liners into undisturbed sod beyond the tip of the auger <br /> The sampler is driven a maximum 18 inches using a 140-pound hammer falling from a <br /> height of 30 inches One sample collected at each sampling interval is retained for <br /> laboratory analyses Soil samples retained for chemical analyses are collected in clean <br /> brass liners, covered with either teflon tape or aluminum foil, capped with plastic end <br /> caps and sealed in plastic zip-lock bags The samples are then placed in a cooler with <br /> either frozen blue ice or ice, logged onto a Chain-of-Custody form and transported to a <br /> State-certified analytical laboratory Each sample is labeled with an indelible-ink <br /> marking pen with protect identification, boring designation, depth, and date The split- <br /> spoon sampler is cleaned between sample intervals with an Alconox wash and rinsed <br /> with clean water, and a final rinse with deionized (distilled) water All downhole drilling <br /> equipment is steam-cleaned between each boring location Wash water is contained in <br /> D O T 55-gallon drums and transferred to a State-approved water reclamation facility <br /> Organic Vapor Screening <br /> Soil samples are screened in the field for volatile organic compounds using a <br /> Photoionization Detector (PID) The test procedure involved measuring a <br /> representative sample from an undisturbed soil sample, placing this subsample in a zip- <br /> lock bag The bag is allowed to warm to ambient temperature for approximately 20-30 <br /> minutes, then the bag is pierced and the head-space within the bag is tested for total <br /> organic vapors, measured in parts per million, (ppm, volume/volume) The instrument <br /> is automatically calibrated internally when powered up using an isobutylene standard <br /> (in air) and a sensitivity factor of 0 56, which relates the photo-ionization sensitivity of <br /> benzene to the sensitivity of isobutylene The PID is also calibrated before leaving for <br /> the field The detection limit of the instrument ranges from 0 1 ppm to 2,000 ppm The <br /> results of these tests are recorded on the boring logs presented in Appendix B It <br /> should be noted that the PID measurements are considered semi-quantitative data <br /> since the instrument detects all organic compounds with ionization potentials less than <br /> 10 eV Heavy organic compounds such as motor oil or diesel fuel are not detected <br />
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