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ARCHIVED REPORTS_XR0011765
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545028
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ARCHIVED REPORTS_XR0011765
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Last modified
12/6/2019 5:02:16 PM
Creation date
12/6/2019 3:05:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011765
RECORD_ID
PR0545028
PE
3528
FACILITY_ID
FA0003919
FACILITY_NAME
VAN DE POL ENTERPRISES
STREET_NUMBER
5491
STREET_NAME
F
STREET_TYPE
ST
City
BANTA
Zip
95304
CURRENT_STATUS
02
SITE_LOCATION
5491 F ST
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1 <br /> i <br /> APEX ENVIROTECH, INC. <br /> STANDARD OPERATING PROCEDURES <br /> j RE: GROUNDWATER PURGING AND SAMPLING <br /> SOP-7 <br /> E <br /> Prior to water sampling, each well is purged by evacuating a minimum of three wetted well-casing volumes of <br /> I <br /> groundwater. When required, purging will continue until either the discharge water temperature, conductivity, <br /> or pH stabilize, a maximum of ten wetted-casing volumes of groundwater have been recovered, or the well is <br /> bailed dry. When practical, the groundwater sample should be collected when the water level in the well E <br /> 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 pump with a <br /> "Teflon" bladder. If the sampling system is dedicated to the well, then the bailer is usually "Teflon," but the <br /> bladder pump is PVC with a polypropylene bladder. In general and depending on the intended laboratory analysis, <br /> 40-miililiter glass, volatile organic analysis (VOA) vials, with "Teflon" septa, are used as sample containers. <br /> 1 <br /> The groundwater sample is decanted into each VOA vial in such a manner that there is no meniscus at the top <br /> of the vial. A cap is quickly secured to the top of the vial. The vial is then inverted and gently tapped to see <br /> if air bubbles are present. If none are present, the vial is labeled and refrigerated for delivery, under strict chain- <br /> of-custody, to the analytical laboratory. Label information should include a unique sample identification number, <br /> job identification number, date, 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 may also be <br /> analyzed or put on hold at the laboratory. When required, a trip blank, prepared at the laboratory, is placed in <br /> the transport cooler. It is labeled similar to the well samples, remains in the cooler during transport, and is 1 <br /> analyzed by the laboratory along with the groundwater samples. In addition, a field blank may be prepared in <br /> the field when sampling equipment is not dedicated. The field blank is prepared after a pump or bailer has been <br /> j either steam cleaned or properly washed, prior to use in the next well, and is analyzed along with the other <br /> samples. The field blank analysis demonstrates the effectiveness of the in-field cleaning procedures to prevent <br /> cross-contamination. <br /> To minimize the potential for cross-contamination between wells, all well development and water sampling ; <br /> equipment not dedicated to a well is either steam cleaned or properly washed between use. As a secondary <br /> precautionary measure, wells are sampled in order of least to highest concentrations as established by available <br /> previous analytical data. <br /> E <br /> In the event the water samples cannot be submitted to the analytical laboratory an the same day they are <br /> collected (e.g., due to weekends or holidays), the samples are temporarily stored until the first opportunity for <br /> E: <br /> submittal either on water ice in a cooler, such as when in the field, or in refrigerator at Apex's office. <br /> 4 <br /> i <br /> ATTACHMEWMP-711ULY 1993 <br /> w <br /> i <br />
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