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ARCHIVED REPORTS XR0001620
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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CLAY
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639
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3500 - Local Oversight Program
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PR0544513
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ARCHIVED REPORTS XR0001620
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Entry Properties
Last modified
6/14/2019 1:07:01 PM
Creation date
6/14/2019 10:43:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001620
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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x 1 } <br /> tt 7 t <br />'1' t ' , I_ � _ x -. -e -. y - - "` i - _r 1 r _ n x i 11`J �- �L • ' I � c ' � ' t h <br /> i <br /> t <br /> t 7 l <br /> . 10 April 2001 <br /> AGE-NC Project No '96-0235 <br />'s Page 2 of 5 <br /> F <br /> 2 2 COLLECTION OF GROUND WATER SAMPLES <br /> Water samples were collected from each purged well using new disposable plastic bailers Each- <br />' t - water sample was transferred into 40-ml VOA vials containing 0 5 ml 18% hydrochloric acrd as a <br /> sample preservative and into 1-liter amber bottles without preservative After collection,the samples <br /> were properly labeled, placed in a chilled container and transported under chain-of-custody to - <br />' McCampbell Analytical, Inc (MAI), a State of California Department of Health Services (DHS)- <br /> certified analytical laboratory, and were analyzed for <br /> f <br /> 1 ` • Total petroleum'hydrocarbons quantified as gasoline'(TPH-g) and as diesel (TPH'd) in <br /> accordance with EPA Methods 5030/8015 and 3550/8015, respectively, <br />' • Volatile aromatic hydrocarbons - benzene, toluene, ethylbenzene and total xylenes (BTEX) <br /> and methyl tertiary-butyl ether (MTBE) in accordance with EPA Method 602/8020, and for <br /> • Fuel oxygenates - di-isopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), MTBE, L <br />' tertiary-amyl methyl ether (TANTE), tertiary butanol (TBA), methanol, ethanol, ethylene <br /> chbromide(EDB) and 1,2-dichloro ethane(1,2-DCA) in accordance with EPA Method 8260 <br /> Modified - <br />' 3.0. FINDINGS <br /> Ground water elevation and flow direction were mferred from field data, hydrocarbon`impact to <br />' ground water was quantified by laboratiory analysis of the ground water samples Field observations, <br /> resultslof laboratory analysis of groundwater samples,and a discussion of data collected during field <br /> work follows ' <br /> f ' ' <br /> 3 1 GROUND WATER GRADIENT AND FLOW DIRECTION <br /> i - <br /> --The casing elevation of each well was previously surveyed relative to a City of Stockton bench mark -- <br />' The elevation of ground water in each well was calculated by subtracting the depth to ground water <br /> from the surveyed casing elevations (Table 1) Depths to ground water,ranged from 15 02 feet to <br /> '18 04 feet below the tops of the well casings Ground water elevations at the site ranged from-9 87 <br />' feet in MW--6A to -11 50 feet mean sea level (MSL) in MW-2 Groundwater elevation increased r <br /> an average of 1 86 feet in the wells MW4 was not monitored during the 13 March 2001 event due <br /> to construction activity in the area of the well <br /> . To infer ground water flow.direction, the ground water elevation data was divided into two sets <br /> based on the well screen'intervals Ground water was between 21 96 and 24 12 feet above the <br /> Advanced GeoEnvironmenta4 Inc <br /> I <br /> { r M <br />
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