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ARCHIVED REPORTS_XR0009339
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545660
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ARCHIVED REPORTS_XR0009339
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Last modified
5/12/2020 3:21:11 PM
Creation date
5/12/2020 2:13:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009339
RECORD_ID
PR0545660
PE
3528
FACILITY_ID
FA0003909
FACILITY_NAME
PORT OF STOCKTON
STREET_NUMBER
2201
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14503001
CURRENT_STATUS
02
SITE_LOCATION
2201 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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4.0 SOIL FIELD SCREENING <br /> A portable photoionization detector (PID), a type of organic vapor analyzer, may be used to test <br /> the presence of volatile organic concentrations in ambient au for the purpose of personnel health , <br /> and safety monitoring during field activities. The PID may also be used to screen selected soil <br /> samples collected from the soil borings The purpose for the field screening of selected soil <br /> samples is to assess the presence of volatile organic compounds in the soil samples ' <br /> The PID measures total volatile organics in the air in parts per million by volume in reference ' <br /> to a selected standard. Calibration of the PID will be performed each day prior to the soil <br /> sampling. <br /> The PID may be used to periodically screen for volatile organics in the air space at the top ' <br /> opening of the Geoprobe tube, after the probe's bottom plug has been removed. The PID <br /> screening method for selected soil samples consists of transferring a soil sample into a new, one- ' <br /> pint plastic zip-Iock bag After about 15 minutes, the bag will be opened and the headspace <br /> quickly screened for the presence of volatile organics. Soil samples used for field screening will <br /> not be submitted to the laboratory for chemical analysis. , <br /> The PID cannot specifically identify each volatile compound, but can be adjusted to be sensitive <br /> to selected volatile organics All PID readings for soil samples and ambient air at the top of the ' <br /> Geoprobe will be recorded on the boring logs Positive readings from the PID screening may <br /> be used for selection of soil samples for chemical analysis <br /> 5.0 DOCUMENTATION <br /> 1 <br /> 5.1 Sample Control Log <br /> Samples collected will be recorded on sample control log sheets (Figure C-1) with indelible ink ' <br /> as a means of uniquely identifying and tracking the samples The log sheets will be placed in <br /> a binder and the sheets will be numbered consecutively. When sampling is completed, the ' <br /> binder and log sheets will be placed in the project file. <br /> 5.2 Chain-of-Custody Procedures , <br /> After samples have been collected and labeled, they will be maintained under chain-of-custody , <br /> procedures. These procedures document the transfer of custody of samples from the field to the <br /> laboratory. ' <br /> A chain-of-custody record (Figure C-2) shall be filled out for each sample sent to the laboratory <br /> for analysis. Information contained on the triplicate carbonless form shall include: <br /> C - 2 D 198117XPROTOCOL WPN <br />
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