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ARCHIVED REPORTS XR0001434
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544196
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ARCHIVED REPORTS XR0001434
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Last modified
2/27/2019 3:57:53 PM
Creation date
2/27/2019 1:55:41 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001434
RECORD_ID
PR0544196
PE
3528
FACILITY_ID
FA0006536
FACILITY_NAME
WELLS FARGO BANK PROPERTY
STREET_NUMBER
1034
STREET_NAME
CENTRAL
STREET_TYPE
AVE
City
TRACY
Zip
94805
APN
23517127
CURRENT_STATUS
02
SITE_LOCATION
1034 CENTRAL AVE
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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• <br /> GETTLER-RYAN INC. <br /> FIELD METHODS AND PROCEDURES <br /> Site Safety 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 dnlimg, <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 stamless 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 aiummum foil, capped, labeled, and place in a cooler with blue ice for preservation A chain-of- <br /> custody form is initiated m 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 staming <br /> f presence or absence of obvious gasolme hydrocarbon odors <br /> g presence or absence of organic vapors detected by headspace analysis <br /> Field Screening of Soil Sam les <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 mvo Ives removing some soil from one of the sample tubes not retained for chemical analysis <br /> and immediately covermg the end of the tube with aplastic 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 venfication of the presence or absence of hydrocarbons <br />
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