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ARCHIVED REPORTS_XR0008405
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3500 - Local Oversight Program
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PR0545859
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ARCHIVED REPORTS_XR0008405
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Last modified
6/3/2020 5:12:37 PM
Creation date
8/15/2019 11:39:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008405
RECORD_ID
PR0545859
PE
3528
FACILITY_ID
FA0003831
FACILITY_NAME
WATERLOO FOODMART
STREET_NUMBER
4315
Direction
E
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215-2305
APN
08710034
CURRENT_STATUS
02
SITE_LOCATION
4315 E WATERLOO RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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STANDARD FIELD PROCEDURES FOR MONITORING WELL INSTALLATION <br /> This document presents standard field methods for drilling and sampling soil borings and <br /> installing, developing and sampling groundwater monitoring wells These procedures are <br /> designed to comply with Federal, State and local regulatory guidelines Specific field procedures <br /> are summarized below <br /> SOIL BORINGS <br /> Objectives <br /> Soil samples are collected to characterize subsurface lrthology, 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 Professional Geologist (P G) or <br /> Professional Engineer(P E) <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 charactenze the subsurface <br /> sediments and for possible chemical analysis Additional soil samples are collected near the <br /> water table and at lithologic changes Samples are collected using lined split-barrel or equivalent <br /> samplers driven into undisturbed sediments at the bottom of the borehole <br /> Drilling and sampling equipment is steam-cleaned prior to drilling and between bonngs to <br /> prevent cross-contamination Sampling equipment is washed between samples with tnsodium <br /> phosphate or 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 <br /> ice, 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 <br /> The tube is capped with plastic end caps and set aside to allow hydrocarbons to volatilize from <br /> the soil After ten to fifteen minutes, a portable volatile vapor analyzer measures volatile <br /> hydrocarbon vapor concentrations in the tube headspace, extracting the vapor through a slit in the <br /> cap Volatile vapor analyzer measurements are used along with the field observations, odors, <br /> stratigraphy and groundwater depth to select soil samples for analysis <br />
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