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ARCHIVED REPORTS_XR0006297
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0528433
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ARCHIVED REPORTS_XR0006297
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Last modified
4/7/2020 1:01:22 PM
Creation date
4/3/2020 4:09:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006297
RECORD_ID
PR0528433
PE
2957
FACILITY_ID
FA0019174
FACILITY_NAME
CHEVRON SERVICE STATION 9-6171
STREET_NUMBER
6633
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
09741048
CURRENT_STATUS
02
SITE_LOCATION
6633 PACIFIC AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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i <br /> I <br /> rr <br /> o it <br /> 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-hter 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 volume measurements of the OVM and the weight measurements of the laboratory <br /> instruments 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 /> aluminum foil is placed on the open end and a polyethylene cap with crossed slits is placed over <br /> it <br /> The field screen sample is allowed to temperature equihbrate 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 tube for approximately 15 to 30 seconds or until the maximum <br /> reading has been recorded on the OVM readout panel <br /> The depth from which the sample came 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 SOP <br />
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