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ARCHIVED REPORTS XR0003527
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0541989
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ARCHIVED REPORTS XR0003527
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Last modified
6/21/2019 8:11:11 PM
Creation date
6/21/2019 3:52:53 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003527
RECORD_ID
PR0541989
PE
2950
FACILITY_ID
FA0024100
FACILITY_NAME
COUNTRY CLUB VALERO
STREET_NUMBER
2575
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
APN
12302012
CURRENT_STATUS
01
SITE_LOCATION
2575 COUNTRY CLUB BLVD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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FUGRO WEST, INC. <br /> STANDARD OPERATING PROCEDURES <br /> RE: EXCAVATION SAMPLING (SOIL AND WATER) <br /> SOP-2b <br /> Soil <br /> Excavation and subsequent soil sampling is performed under the direction of a registered <br /> geologist or civil engineer To reduce the potential for cross-contamination, all excavation <br /> equipment is either steam-cleaned or washed prior to use and between excavations Soil samples <br /> are typically collected directly from the excavation surface or from material removed from the <br /> excavation in a backhoe or excavator bucket A portion of the sampled area or material may be <br /> sealed in a plastic bag, jar, or other suitable container for volatile organic screening with either <br /> a portable photoionization detector, flame ionization detector, or an explosimeter Another <br /> portion of the sample may be used to describe the excavated material <br /> Soil samples for chemical analysis are collected in cleaned, thin-walled brass tubes of varying <br /> diameters and lengths (typically 6 inches long by 2 inches outside-diameter) or other appropriate <br /> cleaned sample container A hand-driven sampler holding an inset sample container may be used <br /> To reduce the potential for cross-contamination between samples, the sampler is cleaned between <br /> each sampling event Upon recovery, the sample container is sealed to minimize the potential <br /> of volatilization and cross-contaminatton prior to chemical analysis Brass soil sampling tubes <br /> are typically closed at each end with plastic caps over Teflon or aluminum foil sheeting The <br /> caps may be sealed with duct tape or similar material lacking inappropriate chemical compounds <br /> The sealed sample is labeled and refrigerated for delivery, under strict chain-of-custody, to the <br /> analytical laboratory <br /> Water <br /> Excavation water samples are not advised, because soil particles typically present may affect the <br /> sample However, if required, water samples are collected either directly from the water surface, <br /> if accessible, by dipping the sampling container, or from a clean bailer or similar sampling device <br /> lowered into the excavation Water samples may be collected from the excavating equipment <br /> bucket, if necessary Depending on the intended analyses, 0 5 to 1-liter plastic or glass <br /> containers, or 40-milliliter glass, volatile organic analysis (VOA) vials, with "Teflon" septa, are <br /> typically used as sample containers <br /> For volatile organic analyses, the water sample is decanted into each VOA vial in such a manner <br /> that there is no meniscus at the top of the vial A cap is quickly secured to the top of the vial <br /> The vial is inverted and gently tapped to see if air bubbles are present If none are present, the <br /> vial is labeled and refrigerated for delivery, under strict chatn-of-custody, to the analytical <br /> laboratory Label information typically includes a unique sample identification number, job <br /> identification number, sampler identification, date, and time <br /> Fugro West Inc <br /> SOP-2b/October 1994 <br />
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