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ARCHIVED REPORTS_XR0006877- CASE 2
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PR0506426
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ARCHIVED REPORTS_XR0006877- CASE 2
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Entry Properties
Last modified
7/27/2020 11:15:13 AM
Creation date
7/27/2020 9:38:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006877- CASE 2
RECORD_ID
PR0506426
PE
2950
FACILITY_ID
FA0007416
FACILITY_NAME
STEPHENS MARINE INC
STREET_NUMBER
345
Direction
N
STREET_NAME
YOSEMITE
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13526011
CURRENT_STATUS
01
SITE_LOCATION
345 N YOSEMITE ST
P_LOCATION
01
QC Status
Approved
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LSauers
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EHD - Public
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t <br /> 29 October 2004 <br /> AGE-NC Project No 97-0351 <br /> ' Page 2 of 4 <br /> ' 2 2 COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> Water samples were collected from each monitoring well using the dedicated, disposable plastic <br /> bailer or Waterra check bailer after allowing the well to achieve a minimum 80%recovery of the pre- <br /> purge water volume The samples from each well were transferred into three 40-milliliter (ml) <br />- - volatile organic analysis(VOA)vials containing 0 5 ml 18%hydrochloric acid solution as a sample <br /> preservative The samples were labeled with the monitoring well designation,date,time of sampling, <br /> and the sampler's initials and transported in a chilled container under chain of custody to Cal Tech <br /> Environmental Laboratories (CTEL), a Department of Health Services (DHS)-certified analytical <br /> ' laboratory for analysis The samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> method 8015M, <br /> • Volatile aromatic compounds benzene, toluene, ethylbenzene, and total xylenes (BTEX) in <br /> accordance with EPA method 8260B, <br /> • Fuel oxygenates tertiary butanol(TBA),di-isopropyl ether(DIPE),ethyl tertiary-butyl ether <br /> (ETBE), tertiary-amyl methyl ether (TAME), and methyl tertiary-butyl ether (MTBE) in <br /> ' accordance with EPA method 8260B, and <br /> • Lead scavengers ethylene dibromide(EDB)and 1,2-dichloroethane(1,2-DCA)in accordance <br /> ' 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 quantified by laboratory analysis of the ground water samples <br /> ' 3 1 GROUND WATER GRADIENT AND FLOW DIRECTION <br /> '- The elevation of ground water in each of the monitoring wells was calculated by subtracting the <br /> depth to ground water from the surveyed relative casing elevations(Table 1) Depths to ground water <br /> averaged about 8 98 feet below surface grade(bsg) Ground water elevations at the site ranged from <br /> 0 95 feet (MW-5) to 107 feet (MW-2) above mean sea level (MSL) The ground water flow <br /> direction at the former UST area was generally toward the northeast with a calculated gradient of <br /> 0 001 foot/foot (ft/ft) During this monitoring event, the ground water elevations were within the <br /> ' screened intervals of the wells Figure 3 illustrates the contoured ground water elevations as <br /> measured on 06 August 2004 <br /> Advanced CeoEnvironmental,Inc <br />
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