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WORK PLANS_FILE 2
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2900 - Site Mitigation Program
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PR0505148
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WORK PLANS_FILE 2
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Last modified
2/5/2020 7:10:14 PM
Creation date
2/5/2020 2:51:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0505148
PE
2950
FACILITY_ID
FA0003950
FACILITY_NAME
SJ COUNTY GARAGE
STREET_NUMBER
130
Direction
N
STREET_NAME
HUNTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
02
SITE_LOCATION
130 N HUNTER ST
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
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I <br /> TlreadweIKMlo <br /> �y <br /> samples were collected from each boring, in both the shallow and deep zones at approximately 30 and <br /> 60 feet bgs. <br /> The soil borings in the first two phases of the Site investigation were drilled by Resonance Sonic Drilling <br /> using a direct-push and hollow stem auger combination drill rig. Soil borings were advanced using a -) <br /> 3 .5-inch diameter drive casing with an inner sample barrel . Continuous soil cores were collected inside <br /> the sample barrel using four-foot disposable acetate liners. After being advanced approximately 4 feet, <br /> the full sample barrel was retrieved while the drive casing was left in place to prevent the hole from <br /> i <br /> collapsing and to prevent cross contamination between the shallow and deep zones. Samples were <br /> i <br /> generally collected at 5-foot intervals from 20 feet below ground surface to depth. - <br /> The soil borings in the last phase of the Site investigation were drilled by Spectrum Exploration Inc. using <br /> a hollow stem auger drill rig. Borings were advanced using 8-inch diameter augers with an 18-inch split <br /> spoon sampler. Soil cores were collected in 1 .5•inch brass tubes inside the sample barrel. Samples were <br /> generally collected at 5-foot intervals from 50 feet bgs to depth. <br /> Soil samples from the continuous cores, brass tubes, and the test pits were screened in the field for the <br /> presence of volatile organic vapors using a portable organic vapor meter (OVM) with a photoionization <br /> detector with a 10. 2-electron-volt lamp. Recorded OVM measurements are presented on the soil <br /> boring logs (Appendix A). - ) <br /> After the sample cores were retrieved and logged, selected tubes were saved for chemical analysis. The <br /> sample tube ends were covered with Teflon"' sheets, sealed with plastic end caps, labeled, and stored in <br /> an ice-cooled chest for delivery to the analytical laboratory. <br /> To facilitate grab groundwater sample collection in the shallow zone, the boring casing was pulled up to <br /> ifs <br /> approximately just above the groundwater elevation, and a temporary one-inch diameter slotted PVC <br /> casing with a 5-foot long screen interval was placed into the boring . To facilitate grab groundwater -_ <br /> sample collection in the deep zone a hydropunch sampler was used with a two- to five-foot screen <br /> interval . Groundwater grab samples were collected using a dedicated disposable polyethylene bailer. All <br /> groundwater samples and selected soil samples were submitted to STL Chromalab, a California state- <br /> certified laboratory for analysis using chain-of-custody protocols. <br /> 6 <br /> 25971201 . DGD 6 February 2008 <br /> J <br /> i <br />
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