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ARCHIVED REPORTS_XR0004371
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2900 - Site Mitigation Program
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PR0506313
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ARCHIVED REPORTS_XR0004371
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Last modified
3/9/2020 7:44:10 PM
Creation date
3/9/2020 9:20:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004371
RECORD_ID
PR0506313
PE
2950
FACILITY_ID
FA0000514
FACILITY_NAME
MAIN STREET SHELL*
STREET_NUMBER
1071
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21707011
CURRENT_STATUS
02
SITE_LOCATION
1071 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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CAMBRIA <br /> STANDARD FIELD PROCEDURES FOR MONITORING WELL INSTALLATION <br /> This document presents standard field methods for drilling and sampling Soil borings and installing, <br /> developing and sampling ground water monitoring wells These procedures are designed to comply with <br /> Federal, State and local regulatory guidelines Specific field procedures are summarized below <br /> SOIL BORINGS <br /> Objectives <br /> Soil samples are collected to characterize subsurface hthology, assess whether the soils exhibit obvious <br /> hydrocarbon or other compound vapor or staining, and to collect samples for analysis at a State-certified <br /> laboratory All borings are logged using the Unified Soil Classification System by a trained geologist working <br /> under the supervision of a California Registered Geologist{RG} <br /> Soil Boring and Sampling <br /> Soil borings are typically drilled using hollow-stem augers or direct-push technologies such as the Geoprobe® <br /> Soil samples are collected at least every five ft to characterize the subsurface sediments and for possible <br /> chemical analysis Additional soil samples are collected near the water table and at lithologic changes <br /> Samples are collected using lined split-barrel of equivalent samplers driven into undisturbed sediments at the <br /> • bottom of the borehole <br /> Drilling and sampling equipment is steam-cleaned prior to drilling and between borings to prevent <br /> cross-contamination Sampling equipment is washed between samples with trisodium phosphate or an <br /> equivalent EPA-approved detergent <br /> Sample Analysis <br /> Sampling tubes chosen for analysis are trimmed of excess soil and capped with Teflon tape and plastic end <br /> caps Soil samples are labeled and stored at or below 4"Con either crushed or dry ice, depending upon local <br /> regulations Samples are transported under chain-of-custody to a State-certified analytic laboratory <br /> Field Screening <br /> One of the remaining tubes is partially emptied leaving about one-third of the soil in the tube The tube is <br /> capped with plastic end caps and set aside to allow hydrocarbons to volatilize from the soil After ten to <br /> fifteen minutes,a portable volatile vapor analyzer measures volatile hydrocarbon vapor concentrations in the <br /> tube headspace,extracting the vapor through a sht in the cap Volatile vapor analyzer measurements are used <br /> along with the field observations, odors, stratigraphy and ground water depth to select soil samples for <br /> analysis <br /> Page i of 3 <br />
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