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ARCHIVED REPORTS_XR0003410
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545426
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ARCHIVED REPORTS_XR0003410
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Last modified
3/6/2020 12:16:57 PM
Creation date
3/6/2020 10:44:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003410
RECORD_ID
PR0545426
PE
3528
FACILITY_ID
FA0003857
FACILITY_NAME
DIAMOND TRANSPORTATION LOGISTIC INC
STREET_NUMBER
2850
Direction
E
STREET_NAME
LOOMIS
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
17910003
CURRENT_STATUS
02
SITE_LOCATION
2850 E LOOMIS RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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24 October 2003 <br /> AGE-NC Project No. 98-0497 <br /> Page 2 of 4 <br /> 2.2. GROUND WATER SAMPLE COLLECTION <br /> Prior to the collection of ground water samples, the depth to ground water was re-measured in each <br /> well to ensure that a minimum of 80% of the initial water volume had recharged. Water,samples <br /> were then collected from each well using a clean,disposable plastic bailer.The waterwas transferred <br /> into one i-liter amber bottle and three chilled 40-m1 volatile organic analysis(VOA)vials containing <br /> 0.5 ml hydrochloric acid(18%)as a sample preservative. After collection,the samples were labeled <br /> and placed in a chilled container for transportation under chain-of-custody to McCampbell <br /> Analytical Laboratories(MAI),a Department of Health Services-certified analytical laboratory. Each <br /> sample was analyzed for: <br /> • Total petroleum hydrocarbons as gasoline and diesel(TPH-g and TPH-d)in accordance with <br /> EPA Method 8015 Modified; and <br /> • Benzene, toluene, ethylbenzene and xylenes (BTEX) in accordance with EPA Method <br /> 8021B. <br /> • Fuel additives including di-isopropyl ether(DIPE),ethyl tertiary-butyl ether(ETBE), methyl <br /> tertiary-butyl ether (MTBE), tertiary-amyl methyl ether (TAME), tertiary-butyl alcohol <br /> (TBA), 1,2-dibromoethane(EDB), 1,2-dichloroethane(1,2-DCA), ethanol and methanol in <br /> accordance with EPA Method 8260B. <br /> 3.0. FINDINGS <br /> Ground water elevation and flow direction were inferred from field data. Hydrocarbon-impact to <br /> ground water was assessed by laboratory analysis of the ground water samples. <br /> 3.1. GROUND WATER ELEVATION AND GRADIENT <br /> Ground water elevations were determined by subtracting the measured depths-to-water from the <br /> surveyed casing elevations. The average ground water elevation on 16 June 2003 was 39.0 feet <br /> below mean sea level (MSL), with the average depth to water at 63.9 feet below casing tops. The <br /> average ground water elevation in the wells was unchanged between the March and June 2003 <br /> monitoring events. Ground water was within the screened interval of each monitoring well. <br /> The water table flow direction at the former UST location was east-northeast under an average <br /> ;radient of 0.002 ft/ft. Figure 3 illustrates the contoured ground water elevations as measured on 16 <br /> June 2003. <br /> Advanced GeoEnvironmental,Inc. <br />
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