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ARCHIVED REPORTS_XR0003213
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0541693
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ARCHIVED REPORTS_XR0003213
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Entry Properties
Last modified
2/6/2020 12:20:05 PM
Creation date
2/6/2020 11:05:56 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003213
RECORD_ID
PR0541693
PE
2960
FACILITY_ID
FA0023897
FACILITY_NAME
TOYOTA TOWN INC
STREET_NUMBER
610
Direction
N
STREET_NAME
HUNTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906033
CURRENT_STATUS
01
SITE_LOCATION
610 N HUNTER ST
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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� v <br /> 0 <br /> A S S O C I A T E S I N C <br /> 4.0 SITE INVESTIGATION ACTIVITIES <br /> All work described herein was performed in accordance with ATC's Workplan for Additional <br /> Soil Boring and Monitoring Well Installation Activities at 610 North Hunter Street, Stockton, <br /> California, dated October 10, 2001, which was approved with minor modifications by SJEHD in <br /> correspondence dated October 24, 2001 <br /> ' 4.1 Geo robe® Drilling Activities <br /> On December 11, 2001, ATC personnel supervised advancement of four soil borings, SB 12 <br /> through SB 16 to first encountered groundwater, approximately 26 to 27 feet bgs The soil <br /> borings were advanced at the locations shown on Figure 2 to evaluate the horizontal extent of <br /> ' petroleum hydrocarbon impacted soil and groundwater <br /> 4.2 Soil Boring Advancement and Sampling <br /> Fisch Environmental, California License C57 683865, advanced the borings using a truck mounted <br /> Geoprobe® narrow diameter ng employing direct push technology Soil samples were collected <br /> from borings SB 12 through SB 16 at five-foot intervals in acetate sampling tubes and were <br /> described according to the Unified Soil Classification System Descriptions of soil types <br /> ' encountered and sample collection intervals are presented on the boring logs contained in Appendix <br /> A Each soil sample was field screened with a Flame Ionization Detector (FID) for the presence of <br /> volatile organic compounds Sample tubes were then sealed at each end using Teflon tape and <br />' plastic end caps, labeled, and placed on ice <br /> 43 Soil Sample Analysis <br /> Selected soil samples were kept on ice and delivered un <br /> P P der chain-of-custody documentation to <br /> State-certified Argon Laboratories Inc (ELAP Cert No 2359) in Ceres, California for chemical <br /> analysis Selected samples were analyzed for TPHg by EPA method 8015, benzene, toluene, <br /> ethyl benzene, and xylenes (BTEX) by EPA method 8020, and methyl tertiary butyl ether <br /> (MTBE), tertiary amyl ether (TAME), ethyl tertiary butyl ether (ETBE), tertiary butyl alcohol <br />' (TBA), di-isopropyl ether (DIPE), 1,2-dichloroethane (1,2-DCA), and ethyl dibromide (EDB) by <br /> EPA method 8260 The analytical results for soil samples are summarized in Table 1 <br /> Laboratory data sheets and chain-of-custody documentation are included in Appendix B <br />' 4.4 <br /> T, Groundwater Sampling and Analysis <br /> Groundwater samples were collected from borings SB 12 through SB 16 at the depth groundwater <br /> was first encountered, approximately 23 feet bgs A Geoprobe® Screen Point 15 Groundwater <br /> Sampler was threaded onto the leading end of the Geoprobe after groundwater had been <br /> w lwordpro1625961reportsloff--site doe 4 <br />
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