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ARCHIVED REPORTS XR0001426
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3500 - Local Oversight Program
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PR0544196
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ARCHIVED REPORTS XR0001426
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Entry Properties
Last modified
2/27/2019 3:45:57 PM
Creation date
2/27/2019 1:49:58 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001426
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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WNg
Tags
EHD - Public
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' tremie pipe or through the center of the hollow-stem augers in one continuous operation from <br /> the bottom of the interval to the top Emplacement of the Portland cement grout was not <br /> accomplished by"free fall" from the ground surface The boring logs show well construction <br /> details The groundwater monitoring wells were developed more than 24 hours after <br /> completion and were sampled at least 24 hours after development as required by the San <br /> Joaquin County Environmental Health Department The development procedure for each <br />' well consisted of pumping or bailing water from the well until the water was visibly clear, the <br /> well went dry, or until a maximum of ten casing volumes had been removed <br />' Organic Vapor Procedures <br /> Soil samples collected at 5-foot depth intervals during drilling were analyzed in the field for <br />' ionizable organic compounds using a photo-ionization detector (PID) with a 10 2 eV lamp <br /> The test procedure involved measuring approximately 30 grams from an undisturbed soil <br />' sample, placing this subsample in a clean clear ziplock type bag The container was warmed <br /> for approximately 20 minutes (in the sun), then the head-space within the container was <br /> tested for total organic vapor, measured in parts per million as benzene (ppm, <br />' volume/volume) The instrument was calibrated prior to drilling using a 100-ppm <br /> isobutylene standard (in air) and a sensitivity factor of 55 which relates the photo-ionization <br /> potential of benzene to that of isobutylene at 100 ppm The results of the field testing was <br /> noted on the boring logs PID readings are useful for indicating relative levels of <br /> contamination, but cannot be used to evaluate hydrocarbon levels with the confidence of <br /> laboratory analyses <br /> Laboratory Procedures <br />' Selected soil vapor, soil samples collected from the soil borings and groundwater samples <br /> collected from the wells were analyzed for the presence of total petroleum hydrocarbons <br />' calculated as gasoline, benzene, toluene, ethylbenzene, and xylenes, and methyl tertiary butyl <br /> ether(MtBE) using modified EPA Methods 8015 and 8020 <br />' Physical Soil Data <br /> Selected soil samples collected from the soil boring were analyzed for determination of <br />' organic carbon content, moisture content, total porosity, bulk density, and grain density <br /> Moisture contents were determined using standards ASTM D-2216 methods Total organic <br /> carbon content was determined by EPA 9060 modified methods Grain and pore volumes <br />' were determined using Boyle's Law double-cell methods with helium as the gaseous <br /> medium Porosity's and densities were then calculated as described in API RP-40, <br /> API Recommended Practice for Core-Analysis Procedure, 1960 Water saturation was also <br /> determined by API RP-40 methods <br /> 910-017 1A/SOIGWRPT A - 2 December 2, 1998 <br />
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