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ARCHIVED REPORTS XR0004701
Environmental Health - Public
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EHD Program Facility Records by Street Name
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M
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MADISON
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423
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3500 - Local Oversight Program
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PR0544427
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ARCHIVED REPORTS XR0004701
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Entry Properties
Last modified
5/7/2019 9:25:08 AM
Creation date
5/7/2019 9:09:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004701
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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S <br /> ' 31 October 2001 <br /> • AGE-NC Project No 95-0144 <br /> Page 2 of 4 <br /> ' intervals using a Hydac water analyzer The recorded field data and logs are included in Appendix A <br /> All purged water was stored in 55-gallon DOT-approved drums on-site <br /> ' <br /> 22 COLLECTION OF GROUND WATER SAMPLES <br /> ' The depth to water was remeasured mmediately following purging each well to gauge the recharge <br /> rate and to assure a minimum of 80 percent recharge prior to sampling although three wells <br /> ' (MW-19A, MW-20B and MW-2I B)were bailed dry and were sampled prior to 80 percent recharge <br /> Water samples were collected from each purged well using new disposable bailers Samples were <br /> transferred into 40-m1 EPA-approved VOA vials containing 0 5 ml 18% hydrochloric acrd as a <br /> ' sample preservative and Into 1-liter amber bottles without preservative The samples were labeled, <br /> stored on ice and transported under chain-of-custody to McCampbell Analytical, Inc (MAI), a <br /> California Department of Health Services (DHS)-certified analytical laboratory Each sample was <br /> ' analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline(TPH-g),total petroleum hydrocarbons <br /> '. quantified as diesel (TPH-d) and total petroleum hydrocarbons quantified as motor oil <br /> (TPH-mo) in accordance with EPA Methods 5030/8015 and 3550/8015, respectively, <br /> • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and methyl tertiary-butyl ether <br /> ' (MTBE) in accordance with EPA Method 8020/602, and <br /> • Fuel oxygenated compounds - tertiary butanol (TBA), ch-isopropyl ether (DIPE), ethyl tert <br /> ' butyl ether(ETBE), tert amyl methyl ether (TAME) and MTBE by EPA Method 8260M <br /> 3.0. FINDINGS <br /> ' Ground water elevation and flow direction were inferred from field data, hydrocarbon-impact to <br /> ground water was quantified from laboratory analysis of the ground water samples <br /> 3 1 RELATIVE GROUND WATER ELEVATION AND GRADIENT <br /> ' The elevation of ground water in each well was calculated by subtracting the depth to water from the <br /> surveyed casing elevation(Table 1) Between May 2001 and August 2001, ground water elevation <br /> decreased between 0 57 feet and 0 92 feet in the monitored wells The approxirxiate hydraulic <br /> ' gradient for,the August 2001 monitoring event was inferred to be 0 003 ft/ft with a flow direction <br /> toward the north Ground water elevation contours derived from data collected on 16 August 2001 <br /> are depicted in Figure 3 Ground water was between approximately 0 29 feet and 5 57 feet above the <br /> 1 <br /> Advanced GeoEnvironmentai,Inc <br /> 1 <br />
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