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SITE INFORMATION AND CORRESPONDENCE_FILE 1
EnvironmentalHealth
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2900 - Site Mitigation Program
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
4/3/2020 2:46:38 PM
Creation date
4/3/2020 2:30:39 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
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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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 to 100 <br /> parts per million of 1-liter of isobutylene. The OX714, which ineasures in parts per million by <br /> 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 Teflon tape and a polyethylene cap <br /> on one end. The brass tube is loosely filled to approximately 1/2 full. Another square of Teflon <br /> tape is placed on the open end and a polyethylene cap with crossed slits is placed over it. <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 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 />
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