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ARCHIVED REPORTS_XR0011438
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545177
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ARCHIVED REPORTS_XR0011438
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Last modified
1/13/2020 5:27:55 PM
Creation date
1/13/2020 4:18:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011438
RECORD_ID
PR0545177
PE
3528
FACILITY_ID
FA0002123
FACILITY_NAME
GREWALS GAS & LIQUOR*
STREET_NUMBER
4100
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95215
APN
14333046
CURRENT_STATUS
02
SITE_LOCATION
4100 E FREMONT ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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I <br /> 1r. <br /> • 24 April 2000 <br />' AGE-NC Project No. 97-0327 <br /> Page 2 of 6 <br /> borings. Soil samples were collected utilizing a California modified split-spoon sampler loaded with <br /> 2-inch by 6-inch brass sleeves. The sampler was driven by dropping a 140-pound weight from a <br /> height of 30 inches. The number of blows required to drive each 6-inch length of the sampler(blow <br />' counts) was recorded on boring logs by an AGE staff geologist. <br /> Soil samples were preserved by covering both ends of the second brass sleeve with Teflon sheets, <br /> capping and sealing with tape. Each preserved sample sleeve was labeled with soil boring location, <br /> depth, time, date and sampler's initials. <br />' Each preserved sample was logged on a chain-of-custody form, placed in a chilled container and <br /> transported to a California Department of Health Services (DHS)-certified laboratory for analysis <br /> in accordance with: <br /> • EPA Method 5030/8015M for total petroleum hydrocarbons quantified as-gasoline and diesel <br />' (TPH-g and TPH-d, respectively); <br /> • EPA Method 8020 for volatile aromatic compounds: benzene, toluene, ethylbenzene and <br /> • xylene (BTEX) with methyl-tertiary butyl ether(MTBE); and <br /> • EPA Method 8260 Modified for tertiary butanol (TBA), di-isopropyl ether(DIPS), ethyl tert <br /> butyl ether(ETBE),tert amyl methyl ether(TAME), and confirmation of MTBE. <br /> The results of the soil analyses are contained in Table 1. <br /> 1 <br /> 2.3. EQUIPMENT DECONTAMINATION <br /> The hollow stem augers were steam cleaned prior to each bore hole advancement. Sampling tools <br /> and brass sleeves used for sample collection were thoroughly washed with a solution of Alconox, <br />' and were thoroughly rinsed with clean tap water prior to each sampling run. At the conclusion of <br /> field activities, all rinseate generated from decontaminating the equipment was placed in properly <br /> labeled D.O.T.-approved model 17H 55-gallon drums and was stored on-site in an area lacking <br />' public access. <br /> 2:4. . . SOIL BORING LOGS <br />' During drilling,'sample duplicates were monitored for the presence of organic vapor using an organic <br /> vapor meter equipped with a photo-ionization detector(PID: Thermo Environmental 580A, 10.0 eV, <br /> calibrated to isobutylene) and were visually described on boring logs in accordance with the Unified <br />' Soil Classification System (USCS). Boring logs are includedas Appendix A. General lithology <br /> Advanced CcoEnvironmcntal,Inc. <br /> 1 <br />
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