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ARCHIVED REPORTS XR0012786
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0012786
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Entry Properties
Last modified
2/15/2019 10:06:37 PM
Creation date
2/15/2019 4:28:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012786
RECORD_ID
PR0522496
PE
2957
FACILITY_ID
FA0015317
FACILITY_NAME
FLAG CITY CHEVRON
STREET_NUMBER
6421
STREET_NAME
CAPITOL
STREET_TYPE
AVE
City
LODI
Zip
95245
APN
05532024
CURRENT_STATUS
02
SITE_LOCATION
6421 CAPITOL AVE
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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SIERRA <br /> SES STANDARD OPERATING PROCEDURE <br /> OVM READINGS - <br /> SES uses an organic vapor meter (OVM) to determine the presence or absence of volatile <br /> organic compounds(VOCs),including benzene. toluene, ethylbenzene,and xylenes in soil samples <br /> chosen for field screening. The OVM uses a photoionization detector(PID) and is calibrated daily <br /> to 100 parts per million of 1-liter of isobutylene. The OVM, which measures in parts per million <br /> by volume (ppmv), is used for qualitative, not quantitative, assessment because the correlation <br /> between the voluine rrieasLirements of the OVM and the weight measurements of the laboratory <br /> instrurnents is not well defined. <br /> A field screen sample is obtained from the brass tube immediately above or below the brass <br /> tube containing the sample selected for possible analysis. The soil to be screened is removed from <br /> the brass tube, and is placed in a pre-cleaned brass tube with aluminum foil and a polyethylene <br /> cap on one end. The brass tube is loosely filled to approximately 1/2 full. Another square of <br /> alLIMinu1-1-1 foil is placed on the open end and a polyethylene cap with crossed slits is placed over <br /> iC. <br /> The field screen sample is allowed to temperature equilibrate for approximately 15 to 30 <br /> minutes in the sun, allowing any VOCs which might be present in the soil to volatilize out into the <br /> brass tube's headspace. The OVM nozzle is then placed inside the sealed brass tube, through the <br /> slits in the cap, in order to measure the VOCs present, if' any, in the headspace. The nozzle <br /> should remain inside the brass tLibe for approximately 15 to 30 seconds or until the maximum <br /> reading has been recorded on the OVM readout panel. <br /> The depth froin which the sample carne and the corresponding OVM reading is recorded <br /> on the original field log sheet. Field observations, OVM and (odor and staining) readings are used <br /> in determining which soil samples are to be analyzed in the laboratory. <br /> OVM.S()P <br />
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