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ARCHIVED REPORTS_XR0012692
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545028
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ARCHIVED REPORTS_XR0012692
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Last modified
12/6/2019 5:54:55 PM
Creation date
12/6/2019 2:59:49 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012692
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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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 minimurn of three well-bore <br /> volumes of groundwater. When required, purging will col-Itinue until either the discharge <br /> water temperature, conductivity or pH stabilize, a maximum of ten well-bore volumes of <br /> groundwater have been recovered or the well is bailed dry, When practical, the <br /> groundwater sample should be taken when the water level[in the well recovers to at least <br /> 80 percent of its static level. <br /> The sampling equipment consists of either a Teflon bailer, PVC bailer, or stainless steel <br /> ling system is dedicated to the well,then <br /> bladder pump with a Teflon bladder. If the samp p is PVC with a polypropylene bladder. <br /> the bailer is usually Teflon, but the bladder pum 40-milliliter glass, volatile <br /> nded laboratory analysis, <br /> In general and depending on the inte pie containers. <br /> organic analyzer (VOA) vials, with Teflon septa, are used as sam <br /> VOA vial in such a manner that there is <br /> The groundwater sample is decanted into each I Th <br /> no meniscus at the top of the via]. A cap is quickly secured to the top of the via e <br /> and gently tapped to see if air bubbles are present. If none are <br /> vial is then inverted <br /> elivery, under strict chain-of-custody, to <br /> rigerated for d <br /> present, the vial is labeled and ref <br /> ique sample identification <br /> aboratory. Label information should include a un <br /> the analytical I <br /> type of analysis requested, and the <br /> number, job identification number, date, time, <br /> sampler's name. <br /> ample is collected from each well. This <br /> For quality control purposes, a duplicate water s <br /> sample is put on hold at the laboratory. When required, a trip blank is prepar d at the <br /> laboratory and placed in the transport cooler. It is labeled similar to the well samples, <br /> remains in the coo!er 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 /> a pump or bailer <br /> t is not dedicated. The field blank is prepared after <br /> sampling equipmen hed, prior to use in the next well, and is <br /> -cleaned or properly was <br /> has been either steam <br /> field blank analysis demonstrates the <br /> analyzed along with the other samples. The ss-contamination. <br /> effectiveness of the in-field cleaning procedures to prevent cro <br /> To minimize the potential for cross-contamination between wells,all well development and <br /> ated to a well is either steam-cleaned or properly <br /> water sampling equipment not dedic <br /> nd precautionary measure, wells are sampled in order <br /> washed between use. As a seco previous analyses. <br /> of least to highest concentrations as established by available <br /> ATTACHMENTISOP-71FEBRUARY 1992 <br />
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