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ARCHIVED REPORTS_XR0012724
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0522692
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ARCHIVED REPORTS_XR0012724
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Last modified
4/2/2020 2:44:05 PM
Creation date
4/2/2020 2:33:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012724
RECORD_ID
PR0522692
PE
2957
FACILITY_ID
FA0015465
FACILITY_NAME
FORMER MONTGOMERY WARDS AUTO SRV CTR
STREET_NUMBER
5400
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
10227008
CURRENT_STATUS
01
SITE_LOCATION
5400 PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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121 <br /> f :..., -' M"3rrmm <br /> s � s <br /> .J° ' <br /> Ate. <br /> 1=b i <br /> 2.4 FIELD INVESTIGATION <br /> ?,.1 I)RIFI,ING Ri�FD SOTTO SAMPT�It7G �'i <br /> on March 28, 1991, two borings (B-5 and B-b) were driiled <br /> and sampled at tho Site (Figure 2) . Boring B-5 was terminated <br /> at a depth of about 31.5 feet below ground surface (bgs) . The <br /> planned termination depth of boring B-b was also approximately <br /> 30 f4-et bgs. flowever, based on elevated concentrations of <br /> hydrocarbon vapor encountered during drilling, boring B-G was <br /> advanced to a depth of 51.5 feet bgs. <br /> The borings were drilled by West Hazmat Drilling Corp. of <br /> Rancho Cordova, California (Licence No. 554979; C-57 Water Well <br /> Drilling) , under the supervision of an EAI engineer and <br /> geologist. The borings were drilled using S-inch diamet. r <br /> continuous flight h.ollow stem augers. The borings were logged <br /> in accordance with the Unified Soil Classification System (see <br /> Appendix A) . <br /> Soil samples were obtained from each boring beginning at <br /> approximately five feet bgs, and at approximately 5-foot <br /> intervals thereafter, until termination. The samples were <br /> collected using six 2.5-inch diameter 3-inch long brass tubes <br /> mounted within a split-spoon drive sampler employed in advance <br /> of the augers. After sample recovery, the ends of the lowermost <br /> tube were covered with aluminum foil and plastic caps taped over <br /> the ends. Prior to use, all tubes were washed in a solution of <br /> Alconox detergent and tap water, double rinsed with tap water, - <br /> and then with distilled water. The samples were labeled with <br /> the sample point identification, date, time and depth interval, <br /> individually sealed in "Ziploc" plastic bags, and immediately <br /> placed into an ice chest chilled with crushed ice as well as <br /> i frozen blue ice. The samples were kept chilled until delivered <br /> to the laboratory for analytical testing. All samples delivered <br /> to the laboratory were logged on chain of custody record forms <br /> (see Appendix B) . <br /> 3 After sample recovery, a Bacharach TLV sniffer calibrated <br /> against a hexane standard was used on soil contained in the <br /> second tube from the bottom of the shoe, at each sampling <br /> interval within the borings, to determine if volatile <br /> hydrocarbon vapors were emanating directly from the soil. Each <br /> sample was placed in an airtight "Ziploc" plastic bag. The <br /> ' samples were allowed to sit in the sun, and then the head space <br /> in the bags was analyzed using the TLV sniffer. The results of <br /> this testing were recorded on the boring logs (see Appendix B) . <br /> The borings were backfilled from termination depth to grade <br /> using a 10:1 ratio of cement to water with 3-5 percent bentonite <br /> added. <br /> Project No. 1232 -2- <br /> FiVV1ROA' EiVT.11,,1UDIT,INC. <br />
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