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ARCHIVED REPORTS XR0012547
EnvironmentalHealth
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1603
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3500 - Local Oversight Program
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PR0543430
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ARCHIVED REPORTS XR0012547
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Last modified
2/5/2019 11:02:05 AM
Creation date
2/5/2019 10:46:50 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012547
RECORD_ID
PR0543430
PE
3528
FACILITY_ID
FA0009377
FACILITY_NAME
CAL TRANS MAINT SHOP 10
STREET_NUMBER
1603
Direction
S
STREET_NAME
B
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16918002
CURRENT_STATUS
02
SITE_LOCATION
1603 S B ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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ST I <br /> n <br /> 8720033A-COT-5 `fVoodward•Ciyde+Consuitants <br /> soils encountered are presented in Appendix A. Soil samples were recovered <br /> by advancing the augers to a point immediately above the sarple interval <br /> and then driving a modified California Sampler with clean brass liner tubes <br /> through the hollow auger stem. The sampler was then winched out of the <br /> auger string and the sample tubes removed and sealed with aluminum foil and <br /> plastic end caps. Generally the second of the three sample tubes in each <br /> interval was retained for chemical analysis. The soil samples were <br /> delivered to the WCC environmental laboratory under Chain-of-Custcdy <br /> control. After removal of soil subsamples for analysis by WCC, the soil <br /> samples were transmitted under Chain-of-Custody control to California <br /> Anlaytical Laboratory for organic lead analysis. The completed Chain <br /> Custody forms are included in Appendix B. Soil samples were visually <br /> inspected in the field for stains and checked for odors. An HNU <br /> photoionization detector was 'used to check soil samples for organic <br /> vapors. Selected soil samples were sealed in ajar, shaken, and the <br /> photoionizer probe used to check the headspace for organic vapors. Many <br /> soil samples were found to have a distinct hydrocarbon odor or yielded a <br /> non-zero reading when tested with a photoionization detector. <br /> Monitoring Wells <br /> Groundwater monitoring wells were constructed in the soil borings at the <br /> completion of drilling. The groundwater wells were constructed with 4-inch <br /> diameter PVC pipe, with 20 foot lengths of well screen perforated with <br /> .020-inch slots extending from 28.5 to 30 feet to 48.5 to 50 feet blow <br /> the wall of the <br /> grade. The annular space between the slotted pipe and <br /> boring was backfilled with No. 3 Monterey sand to approximately 3 to 4 feet <br /> above the perforated section. A 1 to 2-foot bentonite plug was placed <br /> above the sand pack. The annular space from the top of the bentonite plug <br /> to the ground surface was filled with neat cement grout. The wells were <br /> completed with locking boxes at the surface. <br />
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