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ARCHIVED REPORTS_XR0011735
Environmental Health - Public
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PR0515450
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ARCHIVED REPORTS_XR0011735
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Last modified
10/10/2020 11:30:50 PM
Creation date
6/23/2020 3:55:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011735
RECORD_ID
PR0515450
PE
2960
FACILITY_ID
FA0012153
FACILITY_NAME
SOUTH SHORE PARCEL
STREET_NUMBER
0
STREET_NAME
WEBER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
WEBER AVE
QC Status
Approved
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EHD - Public
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Appendix D Direct Push Boring Investigation <br /> Phase II ESA Multi-Modal Station`Six-Block Project' <br /> January 6,2003 <br /> Page 2 of 15 <br /> • Detection borings were Installed along the E Miner Avenue, E Channel Street, N Grant Street, and N <br /> Aurora Street public right-of-ways and on the Union Pacific Railroad right-of-way to evaluate possible <br /> site sources that might have moved off site or from one of the six blocks "Perimeter" detection borings <br /> were Installed along N Stanislaus Street and E Weber Avenue (where underground utilities permitted) In <br /> order to evaluate if off site sources had Impacted the site <br /> The Geoprobc boring procedures consisted of coring through hard surface material such as concrete or <br /> asphalt, followed by advancing the borings with a hand auger to five feet bgs to check for the presence of <br /> buried utilities Once the bonngs had been advanced to five feet with a hand auger, the direct push <br /> sampling equipment was lowered into the holes Continuous soil cores were collected from five feet to 15 <br /> feet bgs and retained for soil sample collection <br /> The detection boring procedures were identical to the Geoprobe procedures to a depth of 15 feet bgs <br /> Between 15 feet and 35 feet bgs, the detection bonngs were advanced with the soil sampler tip closed At <br /> 35 feet bgs, the soil sampler tip was opened and continuous soil cores were collected from 35 to 45 feet <br /> bgs and retained for soil sample collection and geologic logging After advancement of the detection <br /> bonngs to a depth of 45 feet bgs, a temporary well casing was installed in the open boring to allow <br /> groundwater depth measurement and to facilitate groundwater sample collection <br /> If field observations indicated that contamination was present, the Geoprobe borings were advanced <br /> beyond 15 feet bgs and continuous soil cores collected through the extent of impacted soil Continuous <br /> cores were also collected between 15 and 35 feet bgs in the detection borings if contamination was noted <br /> . at 15 feet bgs If contamination was noted in detection borings at 45 feet bgs, continuous cores were <br /> collected beyond 45 feet bgs through the extent of impacted soil <br /> A limited number of hydropunch bonngs were ,,idvanced to evaluate the potential presence of <br /> groundwater contamination at selected locations The hydropunch borings were generally coupled with a <br /> detection or Geoprobe boring The hydropunch boring procedures consisted of direct push advancement <br /> to approximately 40 to 45 feet bgs, unless otherwise noted, and a five to 10-foot retraction of the push <br /> rods to allow groundwater Influx and sample collection <br /> After completion of the Geoprobe, detection and hydropunch boring advancement and associated <br /> sampling activities, all bonngs were backfilled to grade with a neat cement grout Dye was added to the <br /> grout as necessary to match the pre-existing surface completion at each boring location <br /> 3.1 SOIL SAMPLING PROCEDURES AND LABORATORY ANALYSES <br /> Continuous core soil samples were collected from 5 to 15 feet bgs for laboratory analyses from the <br /> Geoprobe and detection borings The soil samples were collected in clean acetate sleeves installed in five- <br /> foot long macro core samplers Three soil samples, each approximately four inches long, were cut trom <br /> the acetate liners at depths of approximately 5, 10, and 15 feet bgs The ends of the acetate liners were <br /> covered with Teflon' sheeting and capped with plastic end caps The samples were labeled for <br /> identification and placed in a cooler chilled with ice The remainder of the acetate liner was opened for <br /> lithologic logging and other observations A grab sample of soil from each recovered acetate liner was <br /> placed in a re-sealable plastic bag for headspace screening of volatile organic vapors with a <br /> phototonization detector (PID) <br /> • <br />
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