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ARCHIVED REPORTS_XR0008899
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0545786
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ARCHIVED REPORTS_XR0008899
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Last modified
6/1/2020 2:36:43 PM
Creation date
6/1/2020 2:15:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008899
RECORD_ID
PR0545786
PE
3526
FACILITY_ID
FA0004969
FACILITY_NAME
CHASE CHEVROLET
STREET_NUMBER
424
Direction
N
STREET_NAME
VAN BUREN
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
424 N VAN BUREN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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3 0 May 2001 <br /> • Y <br /> AGE-NC Project No 95-0143 <br /> Page 3 of 8 <br />' spoon sampler loaded with three pi e-cleaned 2-inch by 6-inch brass sleeves Samples were collected <br /> at five-foot intervals, beginning at 5 feet bsg using a 140-pound h.mnier to advance the sampler <br /> The number of blows required to advance the split-spoon sampler over each 6-inch increment of the <br /> 18-inch sampling Interval was recorded on the boring logs Sampling equipment was washed in an <br /> Alconox solution and rinsed with water prior to each sampling run to mininnize crass-contamination <br /> Soil samples were reserved b covering both ends of the leading or other selected sleeve with <br /> � p Y g <br /> Teflon sheets, capping with plastic and sealing with tape The samples were labeled, stored on Ice <br /> and transported under chain-of-custody to MAI <br />' 25 LOGGING <br /> Soil was extruded from a second brass sleeve and was screened for the presence of organic vapor <br />' using an organic vapor meter (OVM) equipped with a photo-ionization detector (PID Thermo <br /> Environmental 580A, 10 0 eV, calibrated to isobutylene), and the OVM readings were recorded on <br /> the boring log The soil was then visually described in accordance with the Unified Soil <br />' • Classification System <br />' 26 WELL AND BORING COMPLETION <br /> Borings MW-22, MW-23 and MW-24 were completed as ground water monitoring wells MW-22, <br />' MW-23 and MW-24 using two-inch diameter Schedule 40 PVC casing with 0 020-inch slotted <br /> screen, borings EW-3 and EW-4 were completed as groundwater extraction wells EW-3 and EW-4 <br /> using four-inch diameter Schedule 40 PVC casing with 0 020-Inch slotted screen <br /> Soil borings MW-22, MW-23 and MW-24 were advanced to 30 feet bsg, soil borings EW-3 and <br /> EW-4 were advanced to 35 feet bsg Each well was installed using 20 feet of screen from <br />' approximately 10 feet to 3 0 feet bsg in MW-22, MW-23 and MW-24 and from approximately 15 feet <br /> to 35 feet bsg in EW-3 and EW-4 with blank casing extended to the surface <br />' The filter pack for MW-22, MW-23 and MW-24 (No 3 Lonestar sand) was Installed from 8 feet to <br /> 30 feet bsg The filter pack for EW-3 and EW-4 was Installed from 13 feet to 35 feet bsg in the <br /> borings A nominal 2-foot bentonite-pellet plug was then Installed above the filter pack in each well <br />' The bentonite plugs in the wells were hydrated for approximately thirty minutes <br /> The ground water monitoring wells were gi outed to near the surface with portland cement Water- <br /> tight, traffic-rated well boxes were then installed over the wells As-built well diagrams are depicted <br /> . on the boring logs in Appendix D <br /> Advanced GeoEnvzronmental,Inc <br />
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