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COMPLIANCE INFO_1994-1996
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COMPLIANCE INFO_1994-1996
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Last modified
6/30/2021 1:51:44 PM
Creation date
7/3/2020 11:06:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
1994-1996
RECORD_ID
PR0440006
PE
4434
FACILITY_ID
FA0004515
FACILITY_NAME
FRENCH CAMP LANDFILL
STREET_NUMBER
0
STREET_NAME
MANTHEY
STREET_TYPE
RD
City
STOCKTON
Zip
95231
APN
16307035
CURRENT_STATUS
02
SITE_LOCATION
MANTHEY RD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\sfrench
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440006_0 MANTHEY_1994-1996.tif
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EHD - Public
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City of Stockton - French Camp Landfill TL 394-0028-02 <br /> April 28, 1994 Page 3 <br /> 3.0 FIELD PROCEDURES <br /> Field activities are summarized in the following subsections. Standard operating procedures <br /> for relevant field activities are described in Attachment A. <br /> 3.1 Gas Probe Installation. Twining drilled eight soil borings to depths ranging from 10 <br /> to 15 feet BSG using 6-5/8-inch diameter hollow-stem augers. Soil samples were collected <br /> at five-foot intervals beginning at five feet BSG for lithologic purposes only. A Twining <br /> geologist logged the soils in accordance with the Unified Soil Classification System. Boring <br /> logs are present in Attachment B. Drill cuttings were stored on and covered by plastic. Soil <br /> disposal is the responsibility of thb client. <br /> The soil gas probes (SGPT through SGP8)were constructed of 1-inch diameter schedule 80 <br /> polyvinyl chloride well casing and 0.02-inch machine slotted well screen. Casing and well <br /> screen were flush threaded. Each gas probe was screened in the lower five feet. Rubber <br /> stoppers were placed at the top of the screened section and at the top of the casing. <br /> Teflon tubing extends through the rubber stoppers from approximately one foot below the <br /> bottom stopper to approximately one foot above the top stopper. Samples are to be <br /> obtained through the Teflon tubing. Construction diagrams for the soil gas probes are <br /> presented in Attachment C. <br /> Coarse-grained sand was placed from the bottom of the boring to approximately two feet <br /> above the top of the machine slotted casing. Approximately one foot of bentonite pellets <br /> was placed on top of the filter pack, and the remaining annular space was filled with a sand- <br /> cement grout containing three to five percent powdered bentonite. The bentonite pellets <br /> were hydrated prior to the placement of the grout. Steel standpipes were installed to <br /> approximately 1.5 feet above ground surface, secured in place with concrete, and locked. <br /> Drilling and probe installation activities were supervised by a Twining geologist. The <br /> Twining geologist worked under the direct supervision of a California registered geologist. <br /> Ms. Carol Oz of the San Joaquin County Environmental Health Department was on site <br /> during grouting activities. <br /> 3.2 Soil Gas Monitoring. Following probe installation, soil gas concentrations were <br /> measured using a Gastechtor Model No. 1314SMPN calibrated for methane. Sampling <br /> procedures consisted of a five minute warm up for the meter and at least two minutes of <br /> purge time for each probe. <br />
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