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ARCHIVED REPORTS_XR0007963
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0522692
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ARCHIVED REPORTS_XR0007963
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Last modified
4/2/2020 4:55:21 PM
Creation date
4/2/2020 4:13:39 PM
Metadata
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007963
RECORD_ID
PR0522692
PE
2957
FACILITY_ID
FA0015465
FACILITY_NAME
FORMER MONTGOMERY WARDS AUTO SRV CTR
STREET_NUMBER
5400
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
10227008
CURRENT_STATUS
01
SITE_LOCATION
5400 PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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6.0 DISCUSSION <br /> 6. 1 VICINITY OF SEWER LINE AND FORMER USTs <br /> Borings B-7 and B-8 were drilled in the vicinity of the <br /> sewer line and former UST locations. Only minor concentrations <br /> of TPH were detected in sample B-7 @ 51 . No TPH were detected <br /> in soil samples collected from boring B-8. The only VOCs <br /> detected were toluene at concentrations ranging from 0 . 011 to <br /> 0. 017 ppm and xylenes at 0 . 019 ppm. The total lead <br /> concentrations varied from 6 . 63 to 11. 4 ppm. The carbon chain <br /> breakdown for the hydrocarbons contained in soil sample B-7 @ 5 ' <br /> indicate a hydrocarbon range from C11 to C20 with the maximum <br /> being C17-C18 (see Table 2) . <br /> 6. 2 VICINITY OF FUEL ISLANDS <br /> Borings B-9 and B-10 were drilled in the vicinity of the <br /> fuel islands on the east and west sides of PL-7 . Elevated <br /> concentrations of TPH (1, 200 to 3 , 490 ppm) were detected from <br /> samples B-9 @ 15 ' through B-9 @ 301 . TRPH were determined only <br /> in sample B-9 @ 20 ' at 563 ppm. No benzene was detected in any <br /> of the samples tested. Elevated concentrations of toluene, <br /> xylenes and ethylbenzene were also detected in those samples <br /> 9 which had elevated TPH concentrations (see Table 1) . The total <br /> lead concentrations varied from 5. 72 to 13 . 4 ppm. No soluble <br /> lead was detected in the sample (B-10 @ 101 ) which contained the <br /> highest total lead concentration. The carbon chain breakdown <br /> for the hydrocarbons present in sample B-9 @ 20 ' indicate a <br /> hydrocarbon range from C8 to C18, with the maximum occurring in <br /> the C9-C10 range. The C8 concentration is only 106 ppm which <br /> will rule out gasoline as the contaminant. However, the peak <br /> concentration does not correspond to that of the diesel fuel, <br /> and the concentrations of light hydrocarbons exceed that of <br /> diesel. The information obtained from simulated distillation <br /> and analyses of the gas chromatograph for sample B-9 @ 30 ' agree <br /> with those discussed above, and the chromatograph indicates that <br /> the contaminant corresponds to heavy naphtha (see Tables 2 and 3 <br /> and Appendix C) . <br /> Naphthas are derived from both petroleum and coal tar. <br /> r Petroleum naphthas are composed principally of aliphatic <br /> hydrocarbons and are termed "close-cut" fractions. "Medium- <br /> range" and "Wide-range" fractions are made up of 40 to 80% <br /> aliphatic hydrocarbons, 25 to 50% naphtenic hydrocarbons, 0 to <br /> 10% benzene, and 0 to 20% other aromatic hydrocarbons. Coal tar <br /> naphtha is a mixture of aromatic hydrocarbons, principally <br /> toluene, xylenes, and cumene. Benzene, however, is present in <br /> I _ appreciable amounts in those coal tar naphthas with low boiling _ <br /> !- points. Rubber solvent naphtha boils at 750 to 110° C, and coal <br /> tar naphtha at 1600 to 220° C. Naphthas are used as organic <br /> Pro]ect No. 1232 -7- <br /> ENVIRONMENTAL AUDIT,INC® <br />
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