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ARCHIVED REPORTS_XR0002117
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544983
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ARCHIVED REPORTS_XR0002117
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Last modified
11/15/2019 8:40:41 AM
Creation date
11/15/2019 8:04:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002117
RECORD_ID
PR0544983
PE
3528
FACILITY_ID
FA0005197
FACILITY_NAME
GARYS EXXON SERVICE STATION
STREET_NUMBER
909
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
CURRENT_STATUS
02
SITE_LOCATION
909 W HAMMER LN
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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i <br />�WEGIS ENVIRONMENTAL, INC. <br /> STANDARD OPERATING PROCEDURE <br /> RE:GROUNDWATER PURGING AND SAMPLING <br /> SOP-7 <br /> Prior to water sampling, each well is purged b evacuating a minimum of three wetted well-casing <br /> P 9 Y g <br /> volumes of groundwater When required, purging will continue until either the discharge water <br /> temperature, conductivity, or pH stabilize, a maximum of ten well-bore volumes of groundwater have <br /> been recovered, or the well is bailed dry When practical, the groundwater sample should be <br /> collected when the water level in the well recovers to at least 80 percent of its static level <br /> The sampling equipment consists of either a "Teflon" bailer, PVC bailer, or stainless steel bladder <br /> pump with a "Teflon" bladder If the sampling system is dedicated to the well, then the baler is <br /> usually 'Teflon," but the bladder pump is PVC with a polypropylene bladder In general and <br /> depending on the intended laboratory analysis, 40-milliliter glass, volatile organic analysis (VOA) <br /> Ivials, with "Teflon" septa, are used as sample containers <br /> The groundwater sample is decanted into each VOA vial in such a manner that there is no <br /> meniscus at the top of the vial A cap is quickly secured to the top of the vial The vial is then <br /> inverted and gently tapped to see ff air bubbles are present If none are present, the vial is labeled <br /> and refrigerated for delivery, under strict chain-of-custody, to the analytical laboratory Label <br /> Onformation should include a unique sample identification number, lob identification number, date, <br /> time, type of analysis requested, and the sampler's name <br />' For quality control purposes, a duplicate water sample is collected from each well This sample is <br /> put on hold at the laboratory When required, a trip blank is prepared at the laboratory and placed <br /> in the transport cooler It is labeled similar to the well samples, remains in the cooler during <br />' transport, and is analyzed by the laboratory along with the groundwater samples In addition, a <br /> field blank may be prepared in the field when sampling equipment is not dedicated The field blank <br /> is prepared after a pump or bailer has been either steam cleaned or properly washed, prior to use <br />' in the next well, and is analyzed along with the other samples The field blank analysis <br /> demonstrates the effectiveness of the in-field cleaning procedures to prevent cross-contamination <br />' To minimize the potential for cross-contamination between wells, all well development and water <br /> sampling equipment not dedicated to a well is ether steam cleaned or properly washed between <br /> use As a second precautionary measure, wells are sampled in order of least to highest <br />' concentrations as established by available previous analytical data <br /> In the event the water samples cannot be submitted to the analytical laboratory on the same day <br />' they are collected (e g , due to weekends or holidays), the samples are temporarily stored until the <br /> first opportunity for submittal either on ice in a cooler, such as when in the field, or in a refrigerator <br /> at Aegis' office <br /> ATTACHMENT/SOP-7/SEPTEMBER 1992 <br /> 1 <br />
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