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ARCHIVED REPORTS XR0006030
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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Y
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YOSEMITE
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1399
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3500 - Local Oversight Program
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PR0543988
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ARCHIVED REPORTS XR0006030
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Last modified
12/28/2018 10:59:28 AM
Creation date
12/28/2018 10:58:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006030
RECORD_ID
PR0543988
PE
3500
FACILITY_ID
FA0000914
FACILITY_NAME
TIGER EXPRESS STORES
STREET_NUMBER
1399
Direction
E
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
CURRENT_STATUS
01
SITE_LOCATION
1399 E YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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TMorelli
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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 well-bore <br /> volumes of groundwater When required, purging will continue 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 ether a Teflon baler, PVC bailer, or stainless steel <br /> bladder pump with a Teflon bladder If the sampling system is dedicated to the well, then <br /> the bailer is usually Teflon, but the bladder pump is PVC with a polypropylene bladder <br /> In general and depending on the intended laboratory analysis, 40-milliliter glass, volatile <br /> organic analyzer (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, fob identification number, date, time, type of analysis requested, and the <br /> sampler's name <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 analyses <br /> ATTACHMENTISOP 71FEBRUARY 1992 <br />
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