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ARCHIVED REPORTS XR0004676
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544427
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ARCHIVED REPORTS XR0004676
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Entry Properties
Last modified
5/7/2019 9:17:07 AM
Creation date
5/7/2019 8:36:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004676
RECORD_ID
PR0544427
PE
3528
FACILITY_ID
FA0004581
FACILITY_NAME
CHASE CHEVROLET*
STREET_NUMBER
423
Direction
N
STREET_NAME
MADISON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
CURRENT_STATUS
02
SITE_LOCATION
423 N MADISON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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' k 1 <br /> i' <br /> I <br /> 08 December 1998 <br /> ie AGE-NC Project No 95-0144 <br /> l <br /> Page 2 of 7 <br /> ' analytical laboratory Selected samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) and diesel (TPH-d), in <br /> accordance with EPA Methods 5030 and 8015m <br /> • Volatile aromatic hydrocarbons (benzene, toluene, ethylbenzene and total xylenes, BTEX) <br /> with methyl tertiary butyl ether (MTBE) in accordance with EPA Method 8020 <br /> •I ' <br /> Volatile organic compounds and oxygenated compounds ( di-isopropyl ether [DIPS], ethyl <br /> tertiary-butyl ether [ETBE], MTBE,tertiary-amyl methyl ether [TAME] and tertiary butanol <br /> ' [TBA]) in accordance with EPA Method 8260B <br /> 1 22 LOGGING k <br /> ' Soil was extruded from the second brass sleeve and screened for the presence of organic vapor using <br /> 'an organic vapor meter equipped with a photo-ionization detector (PID Thermo Environmental <br /> . 580A, 10 0 eV, calibrated to isobutylene), and the readings were recorded on the boring log The soil <br /> was then visually described in accordance with the Unified Soil Classification System(see Appendix <br /> A- Boring Logs) <br /> 2 3 WELL COMPLETION <br /> Each boring was overdrilled using 10-inch diameter hollow-stern augers to a total depth of SS,feet' <br /> bsg and was dual-completed as ground water monitoring wells Boring MW-19 was completed using <br /> ' two-inch diameter PVC casing with 0 020-inch slotted screen installed from 53 5 feet to 48 5 feet _ <br /> with blank casing e%tended to the surface The filter pack (No 3 Lonestar sand) was installed from <br /> 53 5 feet to 46 5 feet Bentonite"Pel Plug"was installed from 46 5 feet to 33 feet A second screened <br /> ' PVC casing was installed from 31 feet to 1 I feet with blank casing extending to the surface The <br /> filter pack was installed from 33 feet to 8 5 feet and bentonite pellets were installed from 8 5 feet to <br /> 7 5 feet and hydrated A stainless steel bailer was used to surge the well and set the,sand pack prior <br /> ' to the installation of each bentonite plug The well was then grouted from 7 5 feet to the surface with <br /> portland cement A water tight, traffic-rated well box was then installed over the well <br /> v <br /> ' Boring MW-20 was dual-completed with screened intervals installed from 55 to 50 feet bsg and from <br /> 32 to 12 feet bsg using the above-described completion details Boring MW-21 was dual-completed <br /> with screened intervals installed from 53 to 48 feet bsg and from 32 to 12 feet bsg using the above- <br /> described completion details For surveying, monitoring and sampling purposes,the upper screened <br /> . interval for each dual-completed well was labeled"A",while the lower screened interval was labeled <br /> 1 ' <br /> Advanced GeAn%iron mental Inc <br /> k <br />
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