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COMPLIANCE INFO_1986-1995
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2300 - Underground Storage Tank Program
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PR0231070
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COMPLIANCE INFO_1986-1995
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Last modified
1/30/2023 1:21:59 PM
Creation date
6/3/2020 9:43:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
COMPLIANCE INFO
FileName_PostFix
1986-1995
RECORD_ID
PR0231070
PE
2351
FACILITY_ID
FA0006439
FACILITY_NAME
COUNTRY CLUB MOBIL CIRCLE K
STREET_NUMBER
2575
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
CURRENT_STATUS
01
SITE_LOCATION
2575 COUNTRY CLUB BLVD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\UST\UST_2351_PR0231070_2575 COUNTRY CLUB_1986-1995.tif
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EHD - Public
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UG 24 ' 94 ®E; 2�f�M UGR�` W ROSEVILEE FFD M�E Vol <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. Soll <br />samples are typically collected directly, from the excavation surface or from material <br />removed from the excavation in a.backhoe or excavator bucket. A portion 4f the sampled <br />area or material may be sealed in a plastic bag, jar, or other suitable container for <br />volatile organic screening with either a portable photolonization detector, flame ionization <br />detector, or an explosimeter. Another portion of the sample may be used to describe the <br />excavated material. <br />analysisSoil sampies for chemical --brass <br />varying diamet I Ors and lengths (typically 6 Inchoslong by I Inches outside -diameter) or <br />other appropriate = • sample container..•hand-driven sampler holding <br />an Inset <br />sample container may be used To reduce <br />potential for • • • between <br />samples, the sampler Is cleaned between each sampling event. Upon recovery, the <br />samp;ocontainer 13' sealed to Minimize the, potential, of-volatilizatlon and cross- <br />fne-all'on p'-' M, ical a al sis. B ss sbil sampling tubes are typically closed <br />at each end with plastic caps over Tenon or aluminum foil shooting. - The <br />sealed with duct tape or similar material lacking Inappropriate chemical compounds. The <br />sealeds ample Is labeled and refrigerated for deliveryll'urider strict chain -of -custody, to the <br />analytical laboratory. <br />Water <br />Excavation water samples are not advised, because soil particles typically present may <br />affect the sample, However, If required, water samples are collected either directly from <br />the water surface, if accessible, by dipping the sampling container, or from a clean bailer <br />or similar sampling device lowered Into the excavation. Water samples may be collected <br />from ;the excavating equipment bucket, if necessary. Depending on the intended <br />analyses, 0.5 to. 1 -liter plastic or glass containers, or 40 -milliliter glass, volatile organic <br />analysis (VOA) vials, with "Teflon" septa, are typically used as sample containers. <br />For volatile organic analyses, the water sample Is decanted into each VOA vial In such <br />a manner that there Is no meniscus at the top of the vial. A cap is quickly secured to the <br />top of the vial. The vial Is Inverted and gently tapped to see if air bubbles are present. <br />If none are present, the vial is labeled and refrigerated for delivery, under strict chain -of - <br />custody, to the analytical laboratory. Label Information typically includes a unique sample <br />identification number, job Identification number, sampler Identification, date, and time. <br />ATTACMMFJ'iif8 MWAY IOU <br />
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