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2900 - Site Mitigation Program
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PR0508132
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Entry Properties
Last modified
10/4/2018 3:05:06 PM
Creation date
10/4/2018 2:59:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0508132
PE
2957
FACILITY_ID
FA0007953
FACILITY_NAME
CHEVRON #9-5775
STREET_NUMBER
301
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04514002
CURRENT_STATUS
01
SITE_LOCATION
301 KETTLEMAN LN
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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GETTLER-RYAN INC. <br />FIELD METHODS AND PROCEDURES <br />Site Safetv Plan <br />Field work performed by Gettler-Ryan Inc. (GR) is conducted in accordance with GR's Health and Safety Plan <br />and the Site Safety Plan. GR personnel and subcontractors who perform work at the site are briefed on the <br />contents of these plans prior to initiating site work. The GR geologist or engineer at the site when the work is <br />performed acts as the Site Safety Officer. GR utilizes a photoionization detector (PID) to monitor ambient <br />conditions as part of the Health and Safety Plan. <br />Collection of Soil Samples <br />Soil borings are drilled by a California -licensed well driller. A GR geologist is present to observe the drilling, <br />collect soil samples for description, physical testing, and chemical analysis, and prepare a log of the exploratory <br />soil boring. Soil samples are collected from the soil boring with a split -barrel sampling device fitted with <br />2 -inch -diameter, clean brass tube or stainless steel liners. The sampling device is driven approximately 18 inches <br />with a 140 -pound hammer falling 30 inches. The number of blows required to advance the sampler each <br />successive 6 inches is recorded on the boring log. The encountered soils are described using the Unified Soil <br />Classification System (ASTM 2488-84) and the Munsell Soil Color Chart. <br />After removal from the sampling device, soil samples for chemical analysis are covered on both ends with teflon <br />sheeting or aluminum foil, capped, labeled, and place in a cooler with blue ice for preservation. A chain -of - <br />custody form is initiated in the field and accompanies the selected soil samples to the analytical laboratory. <br />Samples are selected for chemical analysis based in part on: <br />a. depth relative to underground storage tanks and existing ground surface <br />b. depth relative to known or suspected groundwater <br />C. depth relative to areas of known hydrocarbon impact at the site <br />d. presence or absence of contaminant migration pathways <br />e. presence or absence of discoloration or staining <br />f. presence or absence of obvious gasoline hydrocarbon odors <br />g. presence or absence of organic vapors detected by headspace analysis <br />Field Screening of Soil Samples <br />A PID is used to perform head -space analysis in the field for the presence of organic vapors from the soil sample. <br />This test procedure involves removing some soil from one of the sample tubes not retained for chemical analysis <br />and immediately covering the end of the tube with a plastic cap. The PID probe is inserted into the headspace <br />inside the tube through a hole in the plastic cap. Head -space screening results are recorded on the boring log. <br />Head -space screening procedures are performed and results recorded as reconnaissance data. GR does not <br />consider field screening techniques to be verification of the presence or absence of hydrocarbons. <br />A-1 <br />
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