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REMOVAL_1996
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PR0232372
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REMOVAL_1996
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Last modified
5/24/2021 11:27:21 AM
Creation date
11/5/2018 1:34:32 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
REMOVAL
FileName_PostFix
1996
RECORD_ID
PR0232372
PE
2381
FACILITY_ID
FA0003631
FACILITY_NAME
ONE CANLIS
STREET_NUMBER
24
Direction
S
STREET_NAME
HUNTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14914024
CURRENT_STATUS
02
SITE_LOCATION
24 S HUNTER ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\rtan
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\MIGRATIONS\H\HUNTER\24\PR0232372\REMOVAL 1996.PDF
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EHD - Public
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k" KLEINEELDER <br /> 3 FIELD ACTIVITIES <br /> 3.1 DRILLING AND SOIL SAMPLING <br /> On November 6, 1992, one angle boring (B-1) and four vertical soil borings (B-2 through B-5) <br /> — were drilled adjacent to the tank. Soil boring B-1 was drilled at a 45 degree angle from <br /> vertical, and soil samples were collected (or attempted) every 5 feet to a termination depth of <br /> 27 auger feet (19 vertical feet). Soil samples were collected every 5 feet (starting at 10 feet) to <br /> a termination depth of 25 feet in vertical borings B-2 through B-5. Table 1 summarizes the <br /> sample locations and depths. <br /> The borings were advanced with a truck-mounted drill rig equipped with 8-inch hollow stem <br /> augers. While drilling, an experienced environmental geologist logged the boreholes, <br /> classified the soil, and collected soil samples for field screening and chemical analysis. In <br /> general, the soil consisted of backfill pea gravel to a depth of 13 feet. Interbedded sand, silty <br /> sand, and silt were encountered between 13 and 25 feet. No free ground water was <br /> encountered in the borings. A copy of the Unified Soil Classification System (used to identify <br /> the soil), a boring log legend and logs for each boring are included in Appendix A. Detailed <br /> procedures concerning the soil borings and sampling methodology are presented in <br /> Appendix B, Kleinfelder Field Activities Protocol. <br /> The locations of the tank and soil borings are shown on Plate 2, Boring Location Map. A <br /> copy of the approved boring permit is included in Appendix C. <br /> 3.2 QUALITATIVE FIELD SCREENING <br /> To provide a qualitative indication of volatile organic compounds, an organic vapor detector <br /> utilizing a flame-ionization detector (FID) was used to field screen the samples collected from <br /> — each boring. The FID measures total ionizable organic compounds in the air in parts per <br /> million by volume (ppmv). <br /> Each sample was screened in the field, and the FID readings were recorded on the boring logs. <br /> Table 1 summarizes the FID measurements for each sample. The samples collected from B-1 <br /> through B-4 had FID readings of 0 ppmv. FID readings of 2, 20 and 15 ppmv were recorded <br /> for the three soil samples collected from B-5 at 15, 20 and 25 feet beneath the ground surface. <br /> FR8-92-211 Page 4 of 8 24-220191-A00 <br /> Copyright 1992 Kleinfelder, Inc. <br />
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