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ARCHIVED REPORTS XR0007682
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544653
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ARCHIVED REPORTS XR0007682
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Last modified
7/11/2019 7:47:09 PM
Creation date
7/11/2019 2:46:08 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007682
RECORD_ID
PR0544653
PE
3528
FACILITY_ID
FA0004695
FACILITY_NAME
BRIDGESTONE/FIRESTONE #3573
STREET_NUMBER
400
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95201
APN
13907009
CURRENT_STATUS
02
SITE_LOCATION
400 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Mr Knoll <br />' February 19, 1999 <br /> Page 3 <br /> DRILLING AND SOIL SAMPLING <br /> On December 21, 1998, two soil borings(BFS-1 and BFS-2) were drilled using a hollow stem auger drilling <br /> ng, under the supervision of a QST geologist, to a depth of 20 and 28 feet bgs, respectively The drilling was <br /> continued an additional two feet in each boring, using a direct push method to conduct groundwater sampling <br /> The boring locations are shown on Figure 2 During drilling, soil samples were collected at 5-foot intervals <br /> I for geologic description and organic vapor monitoring Soil samples were collected in brass sleeves and <br /> retained for chemical analysis Typical drilling, soil sampling and organic vapor monitoring procedures and <br /> equipment are described in Appendix A <br /> A 3a inch slotted PVC pipe was covered in well sock, to filter the silty fines and placed in the borehole for <br /> groundwater sampling purposes The well sock was used due to the presence of sandy fine material <br /> Groundwater was sampled using a microbader in each of the temporary wells No odor was detected during <br />' groundwater sampling Groundwater samples were labeled and placed in appropriate laboratory containers, <br /> and chain of custody documents completed <br />' Soil cuttings from the drilling were placed in 55-gallon DOT drums, labeled and remain at the site pending <br /> laboratory analysis results The cuttings will be transported to a disposal facility for incineration <br /> Documentation will be provide upon completion of tins activity <br /> 10 LABORATORY ANALYSIS <br /> The soil and groundwater samples were delivered under proper chain-of-custody procedures to Kiff Analytical <br /> Inc , a state-certified laboratory located in Davis, California, for analysis Two soil samples were selected <br /> by Mr Knoll of the SICPHS-EHD for analysis based on vapor readings and location of the sample with <br /> respect to groundwater (within the capillary zone) Mr Knoll requested that soil and groundwater samples <br /> be analyzed for petroleum hydrocarbons, constituents, and oxygenates included the following <br /> Total Petroleum Hydrocarbons as gasoline(EPA Method 8015-modified) <br />' Benzene, Toluene, Ethylbenzene, and Total Xylenes (BTEX) (EPA Method 8020) <br /> Seven Oxygenates-Ternary Butyl Ether (ETBE), Methyl Tertiary Butyl Ether (MTBE), Di-isopropyl ether <br /> (D1PE), Ethyl Tertiary Butyl Ether (ETRE) and Tertiary Amyl Methyl Ether (TAME), Tert butanol, <br /> Methanol, and Ethanol (EPA Method 8260) <br />' One soil sample was selected for analysis by the following protocols for possible future use in a health risk <br /> assessment <br /> Total Organic Carbon using method ASTM 02716 <br /> Porosity by Phase Relationships <br /> Hydraulic conductivity <br /> 1 <br /> SITE ASSESSMENT FINDINGS <br /> Moist to wet silty sand was found un Boring BFS-1 from 25 5 to 28 feet bgs Groundwater was encountered <br /> in the sand unit and soil sampling was terminated at 28 feet bgs In Boring BFS-2, groundwater was <br />' encountered in the silty sand wit and soil sampling terminated at 20 feet bgs The soil types observed at the <br />
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