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ARCHIVED REPORTS XR0001789
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544475
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ARCHIVED REPORTS XR0001789
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Last modified
5/17/2019 3:38:58 PM
Creation date
5/17/2019 3:29:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001789
RECORD_ID
PR0544475
PE
3528
FACILITY_ID
FA0003602
FACILITY_NAME
TESORO (SHELL) 68151
STREET_NUMBER
35
Direction
N
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04318003
CURRENT_STATUS
02
SITE_LOCATION
35 N CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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AEGIS ENVIRONMENTAL, INC. <br /> STANDARD OPERATING PROCEDURE <br /> RE: GROUNDWATER PURGING AND SAMPLING <br /> SOP-7 <br /> Prior to water sampling, each well is purged by evacuating a minimum of three wetted <br /> well-casing volumes of groundwater. When required, purging will continue until either the <br /> discharge water temperature, conductivity, or pH stabilize, a maximum of ten well-bore <br /> volumes of groundwater have been recovered, or the well is bailed dry. When practical, <br /> the groundwater sample should be collected when the water level in the well recovers to <br /> at least 80 percent of its static level. <br /> The sampling equipment consists of either a "Teflon" bailer, PVC bailer, or stainless steel <br /> bladder pump with a "Teflon" bladder. If the sampling system is dedicated to the well, <br /> then the bailer is usually "Teflon," but the bladder pump is PVC with a polypropylene <br /> bladder. In general and depending on the intended laboratory analysis, 40-milliliter glass, <br /> volatile organic analysis (VOA) vials, 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 <br /> no meniscus at the top of the vial. A cap is quickly secured to the top of the vial. The <br />. vial is then inverted and gently tapped to see if air bubbles are present. If none are <br /> present, the vial is labeled and refrigerated for delivery, under strict chain-of-custody, to <br /> the analytical laboratory. Label information should include a unique sample identification <br /> number, job identification number, date, time, type of analysis requested, and the <br /> sampler's name. <br /> i <br /> For quality control purposes, a duplicate water sample is collected from each well. This <br /> sample is put on hold at the laboratory. When required, a trip blank is prepared at the <br /> laboratory and placed in the transport cooler. It is labeled similar to the well samples, <br /> remains in the cooler during transport, and is analyzed by the laboratory along with the <br /> groundwater samples. In addition, a field blank may be prepared in the field when <br /> sampling equipment is not dedicated. The field blank is prepared after a pump or bailer <br /> has.been either steam cleaned or properly washed, prior to use in the next well, and is <br /> analyzed along with the other samples. The field blank analysis demonstrates the <br /> 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 <br /> water sampling equipment not dedicated to a well is either steam cleaned or properly <br /> washed between use. As a second precautionary measure, wells are sampled in order <br /> of least to highest concentrations as established by available previous analytical data. <br /> In the event the water samples cannot be submitted to the analytical laboratory on the <br /> same day they are collected (e.g., due to weekends or holidays), the samples are <br /> temporarily stored until the first opportunity for submittal either on ice in a cooler, such <br /> as when in the field, or in a refrigerator at Aegis' office. <br /> ATTACHMENT/SOP-7/SEPTEMBER 1992 <br />
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