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ARCHIVED REPORTS_XR0008896
Environmental Health - Public
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EHD Program Facility Records by Street Name
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VAN BUREN
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3500 - Local Oversight Program
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PR0545786
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ARCHIVED REPORTS_XR0008896
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Last modified
6/1/2020 2:31:55 PM
Creation date
6/1/2020 2:14:58 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008896
RECORD_ID
PR0545786
PE
3526
FACILITY_ID
FA0004969
FACILITY_NAME
CHASE CHEVROLET
STREET_NUMBER
424
Direction
N
STREET_NAME
VAN BUREN
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
424 N VAN BUREN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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I <br />' 07 May 2003 <br /> • AGE-NC Project No 95-0143 <br />' Page 3 of 5 <br /> 2 2 2 Well Completion <br /> I <br /> Borings OSW-1 through OSW-17 were completed as ozone sparge wells using 30-mch KVA- <br />' manufactured ozone sparge points with 0 75-inch PVC blank casing extended to near surface grade <br /> The filter pack (No 2116 Lonestar sand) was installed from approximately 25 feet to 21 feet bsg A <br /> nominal 2-foot bentonite pellet plug was then installed above the filter pack The wells were then <br /> Igrouted to near surface grade with portland neat cement <br /> A water-tight,traffic-rated well box was installed over OWS-I through OWS-17 The well locations <br /> Iare shown on Figure 2 Ozone sparge well construction is illustrated on Figure 5 <br />' 3.0. FINDINGS <br /> Ground water elevation was calculated and flow direction was inferred from field data, the <br /> hydrocarbon impact to ground water was quantified from laboratory analysis <br /> I • 3 1 GROUND WATER ELEVATION AND GRADIENT <br /> During the December 2002 monitoring event, the average depth to ground water at the site was <br /> 17 62 feet bsg Ground water was within the screened intervals of wells MW-10, MW-14 through <br /> MW-17 and MW-22 through MW-24, ground water ranged from 1 77 feet to 5 16 feet above the <br /> screened interval in the other four monitoring wells <br /> The elevation of ground water in the twelve wells was calculated by subtracting the depth to water <br /> I from the surveyed casing elevation (Table 1) The average ground water elevation was 8 19 feet <br /> below mean sea level(MSL), a decrease of 0 48 feet since the September 2002 monitoring event The <br /> inferred ground water flow direction was toward the northeast with a gradient of 0 001 foot/foot <br /> IGround water elevation contours for the December 2002 monitoring event are illustrated in Figure 3 <br /> 3 2 ANALYTICAL RESULTS OF WATER SAMPLES <br /> During the December 2002 monitoring event, TPH-g was detected in samples collected from <br /> Imonitoring wells MW-3, MW-6 and MW-9 at concentrations ranging from 120 µg/1 (MW-6) to <br /> 170,000 µg/1 (MW-3) Various BTEX compounds were detected in the same wells at concentrations <br /> as high as 4,600 gg/1 benzene, 51,000 }tg/l toluene,4,500 µg/l ethylbenzene and 27,000 µg/1 xylenes, <br /> in sample MW-3 Figure 4 illustrates the approximate extent of TPH-g and benzene contamination <br /> • in ground water <br /> Advanced GeoEnvironmental,Inc <br /> I <br />
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