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WORK PLANS_FILE 1
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WORK PLANS_FILE 1
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Last modified
3/6/2020 1:48:30 PM
Creation date
3/6/2020 1:34:31 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
FILE 1
RECORD_ID
PR0506186
PE
2950
FACILITY_ID
FA0007258
FACILITY_NAME
RIPON SHELL
STREET_NUMBER
341
Direction
E
STREET_NAME
MAIN
STREET_TYPE
ST
City
RIPON
Zip
95366
APN
26114007
CURRENT_STATUS
01
SITE_LOCATION
341 E MAIN ST
P_LOCATION
99
P_DISTRICT
005
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 <br /> with 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 lithology, assess whether the soils exhibit <br /> obvious hydrocarbon or other compound vapor or staining, and to collect samples for analysis at a <br /> State-certified laboratory. All borings are logged using the Unified Soil Classification System by <br /> a trained geologist working 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 <br /> Geoprobe®. Soil samples are collected at least every five ft to characterize the subsurface sediments <br /> and for possible chemical analysis. Additional soil samples are collected near the water table and <br /> at lithologic changes. Samples are collected using lined split-barrel or equivalent samplers driven <br /> into undisturbed 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 <br /> an equivalent EPA-approved detergent. <br /> Sample Analysis <br /> Sampling tubes chosen for analysis are trimmed of excess soil and capped with Teflon tape and <br /> plastic end caps. Soil samples are labeled and stored at or below 4°C on either crushed or dry ice, <br /> depending upon local regulations. Samples are transported under chain-of-custody to a State- <br /> 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 <br /> tube is capped with plastic end caps and set aside to allow hydrocarbons to volatilize from the soil. <br /> After ten to fifteen minutes,a portable volatile vapor analyzer measures volatile hydrocarbon vapor <br /> concentrations in the tube headspace, extracting the vapor through a slit in the cap. Volatile vapor <br /> analyzer measurements are used along with the field observations, odors, stratigraphy and ground <br /> water depth to select soil samples for analysis. <br /> Page 1 of 3 <br />
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