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ARCHIVED REPORTS XR0002712
Environmental Health - Public
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EHD Program Facility Records by Street Name
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HARDING
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2900 - Site Mitigation Program
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PR0506390
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ARCHIVED REPORTS XR0002712
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Entry Properties
Last modified
5/6/2019 2:20:22 PM
Creation date
5/6/2019 2:16:59 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002712
RECORD_ID
PR0506390
PE
2950
FACILITY_ID
FA0007389
FACILITY_NAME
MINI STOP
STREET_NUMBER
244
Direction
W
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
13708014
CURRENT_STATUS
01
SITE_LOCATION
244 W HARDING WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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08 October 2003 <br /> AGE-NC Project No. 98-0504 <br /> Page 5 of 7 <br /> Then a dedicated, inertial Waterra pump was used to remove 20 gallons of water from the wells. <br /> Temperature,pH and conductivity of the purged water were measured at one-gallon intervals using <br /> an Oakton water analyzer during purging; the values had generally stabilized by the end of the <br /> purging process (Appendix Q. Purged water was stored on-site in 55-gallon, Department of <br /> Transportation-approved drums. <br /> AGE surveyed a reference point on the top of each ground water monitoring well casing at the site <br /> to the nearest 0.01-foot relative local rnonitoringwells from the subsurface investigation at 348 West <br /> Harding Way and against the City of Stockton Bench Mark No. HS0391, at 14.47 feet above mean <br /> sea level (MSL) (Appendix Q. <br /> 3.5. COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> Ground water samples were collected from the monitoring wells using disposable polyethylene <br /> bailers; these bailers were disposed of after one use and require no decontaminating, thereby <br /> minimizing cross contamination due to sampling devices. Each water sample was transferred into <br /> Mthree 40-m1 EPA-approved volatile organic analysis (VOA) vials containing 0.5 ml 18% HCl as a <br /> sample preservative.After collection,the samples were labeled and placed in a chilled container for <br /> transportation under chain-of-custody to Cal Tech Environmental Laboratory(CTEL), a California <br /> Department of Health Services-certified Laboratory in Paramount, California. Each sample was , <br /> analyzed for: <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Method 8015 Modified; <br /> • Benzene,toluene,ethylbenzene and total xylenes(BTEX)in accordance with EPA Method <br /> 8260B; and Fuel additive-compounds, including di-isopropyl ether(RIPE), ethyl-tertiary- <br /> butyl ether(ETBE),methyl-tertiary-butyl ether(MTBE),tertiary-amyl methyl ether(TAME), <br /> and t-butyl alcohol (TBA), 1,2-dichloroethane (1,2-DCA), 1,2-dibromoethane (EDB), <br /> ethanol and methanol in accordance with EPA Method 8260B. <br /> 4.0. FINDINGS <br /> Ground water elevation, flow direction, and gradient were determined from field data collected on <br /> 07 April 2003;the contaminant impact ground water was quantified by the laboratory analytical data. <br /> Advanced GeoEnvironmentai,Inc. <br />
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