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ARCHIVED REPORTS XR0007791
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0505525
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ARCHIVED REPORTS XR0007791
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Last modified
7/15/2019 4:48:29 PM
Creation date
7/15/2019 4:18:32 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007791
RECORD_ID
PR0505525
PE
2953
FACILITY_ID
FA0002387
FACILITY_NAME
KEYSTONE AUTOMOTIVE INDUSTRIES INC
STREET_NUMBER
632
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14907033
CURRENT_STATUS
02
SITE_LOCATION
632 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Ill 1195 M11 48 WFM Laptop FAX William F McClenney RG REA Paye 4 of 5 <br /> I& Robert Huntley <br /> 11 January 1995 <br /> Page 3 <br /> The re-sampling effort took place on 22 December 1994 On 27 December 1994, RFA received the <br /> TPHg/BTEX analytical results This sample was reported to contain ethylbenzene at a concentration of <br /> 0 31 ug/L (reporting limit of 0 30 ug/L) and total xylenes at a concentration of 0 74 ug/L (reporting limit <br /> of 0 60 ug/L) The primary Maximum Contaminant Linut (MCL) used by the Califonua Department of <br /> Health Services(CA-DOHS)for ethylbenzene is 680 ug/L with the Federal MCL reported to be 700 ug/L <br /> In the case of total xylenes, the CA-DOHS MCL is 1,750 ug/L and the Federal MCL is 10,000 ug/L <br /> Therefore both results from MW4 are well below both the state and Federal MCLS All other analytes <br /> were reported to be below their respectrve method reporting limits <br /> CONCLUSIONS <br /> At this point in time,it is possible to draw the following conclusions from the available data <br /> • there appears to be no detectable impact from either diesel or gasoline range hydrocarbons in the <br /> soil samples collected above the capillary fringe in MW4 This would tend to place this location <br /> outside of the presumed location of the known gasoline fuel leak located west of MW4, <br /> • an as yet unknown material, which may have been tentatively identified as motor oil in the <br /> capillary fringe soil sample, and which may also be related to the odors described by personnel <br /> present during well development and sampling activities, appears to be present either in <br /> groundwater or in a clayey layer found near the water table surface At present there is no <br /> . definitive connection between the odors detected m well development and sampb ng purge waters <br /> and the material identified in sample SMW-46 5, though there would appear to be such a <br /> connection, <br /> o analytical results compared with groundwater gradients calculated from each well sampling <br /> episode indicate that the samples withdrawn from MW4 appear to indicate that the downgradiem <br /> extent of groundwater impact has been defined Well MW4 appears to be on the very detectable <br /> edge of groundwater impact, but not on a consistent basis as evinced by the two <br /> samp1mg/arWytical events conducted over a 16 day interval, <br /> • organic lead analyses in both soils and groundwater extracted from MW-4 failed to detect the <br /> present of this material This suggests that organic lead is not present at this location. This <br /> evidence is not definitive as to the possible ongm of the gasoline impact as it appears to have been <br /> obtained outside of the presumed location of the soil bound plume and apparently on the"feather" <br /> edge of the groundwater impact More data will be necessary to formulate a conclusion as to <br /> ongin of both plumes <br /> At this point in time, no further downgradient exploration for the extents of groundwater impact would <br /> appear to be warranted On that basis, we propose completing the report of installation of MW4 as a PIER <br /> report after receipt of the remaining analytical data We do not advise further downgradient well <br /> installations to chase the downgradient extent of the gasoline fuel groundwater impact. <br />
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