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WORK PLANS_CASE 2 FILE 2
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WORK PLANS_CASE 2 FILE 2
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Last modified
3/9/2020 10:45:17 AM
Creation date
3/9/2020 8:56:37 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 2 FILE 2
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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. CAMBRIA <br /> STANDARD FIELD PROCEDURES FOR MONITORING WELLS <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 /> i <br /> SOIL BORINGS <br /> Objectives <br /> 'Soil samples are collected to characterize subsurface lithology, 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 <br /> working under the supervision of a California Registered Geologist(RG). <br /> -Soil Boring and Sampling <br /> i <br /> Soil borings are typically drilled using hollow-stem augers or direct-push technologies such as the <br /> Geoprobe®. Soil samples are collected at least every five ft to characterize the subsurface sediments and <br /> ;for possible chemical analysis. Additional soil samples are collected near the water table and at lithologic <br /> changes. Samples are;collected using lined split-barrel or equivalent samplers driven into undisturbed <br /> ;sediments at the 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°C on 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 <br /> the tube headspace,extracting the vapor through a slit in the cap. Volatile vapor analyzer measurements are <br /> fused along with the field observations, odors, stratigraphy and ground water depth to select soil samples for <br /> ,analysis. <br /> II <br /> I <br /> Page 1 of 3 <br /> ii <br />
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