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ARCHIVED REPORTS_XR0008880
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0543607
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ARCHIVED REPORTS_XR0008880
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Last modified
10/10/2020 10:42:12 PM
Creation date
7/9/2020 10:24:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008880
RECORD_ID
PR0543607
PE
3528
FACILITY_ID
FA0006343
FACILITY_NAME
STOCKTON MOBIL 3*
STREET_NUMBER
2358
Direction
E
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
14118221
CURRENT_STATUS
02
SITE_LOCATION
2358 E WATERLOO RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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ENCLOSURE A <br /> SAMPLING TECHNIQUES <br /> Proper sampling techniques were followed to assure that samples represented actual field <br /> conditions and that samples were labeled, preserved, and transported properly to retain sample <br /> integrity This exhibit describes procedures which were followed by Acton • Mickelson • <br /> van Dam, Inc (AMV), during collection of samples of subsurface soil and ground water <br /> Sampling guidance documents from the American Society of Testing and Materials (ASTM), <br /> U S Environmental Protection Agency (EPA), and California Department of Health Services <br /> (DHS) were followed for all sampling procedures Actual sampling procedures employed were <br /> based on field conditions and may differ from those described here <br /> 1.0 EXPLORATION BORING/SOIL SAMPLING PROCEDURES <br /> Soil borings and soil sampling were performed under the direction of an AMV geologist The <br /> soil borings were advanced using a truck-mounted, hollow-stem auger drill ng and a hand auger <br />. Soil samples were collected at 5-foot vertical intervals Soil sampling was done in accordance <br /> with ASTM 1586-84 Using this procedure, three 2-inch-diameter, 6-inch-length, brass tubes <br /> were placed in a California-type split-barrel California-type sampler The sampler was driven <br /> into the soil by a 140-pound weight falling 30 inches After an initial set of 6 inches, the <br /> number of blows required to drive the sampler an additional 12 inches, known as penetration <br /> resistance or the "N" value, was recorded on the respective boring log The "N" value is used <br /> as an empirical measure of the relative density of cohensionless soils and the consistency of <br /> cohesive soils <br /> Upon recovery of the split-barrel sampler, the brass tubes containing the soil were removed <br /> One of the three brass tubes was sealed at the ends with Teflon tape and plastic end caps The <br /> sample was labeled with an identification number, time, date, location, and requested laboratory <br /> analysis The sample was then placed in a plastic bag and stored at approximately 40 Celsius <br /> (C) in an ice chest for transport to the laboratory Sample custody procedures outlined in <br /> Section 4 0 of this exhibit were followed <br /> Soil in one of the brass tubes was extracted upon recovery, placed in a plastic bag, and sealed <br /> for later screening for organic vapors using a photoionization detector (PID) The remaining <br /> portion of the soil sample was examined and a complete log of soil conditions was recorded on <br /> a soil boring log (Enclosure A) using the Unified Soil Classification System (Enclosure B) The <br /> soil was examined for grain size, color, and moisture content <br />• The split-barrel sampler was cleaned to prevent cross-contamination for each sampling interval <br /> using procedures described in Section 2 0 of this appendix <br />
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