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ARCHIVED REPORTS XR0010073
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544793
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ARCHIVED REPORTS XR0010073
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Entry Properties
Last modified
11/19/2024 10:19:03 AM
Creation date
9/3/2019 1:27:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010073
RECORD_ID
PR0544793
PE
3528
FACILITY_ID
FA0006237
FACILITY_NAME
HONEST AUTO SALE AND REPAIR
STREET_NUMBER
595
Direction
E
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
23337004
CURRENT_STATUS
02
SITE_LOCATION
595 E ELEVENTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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r� <br /> Regional lithologic lateral and vertical variation are present in the shallow aquifer strata <br /> and underlying confining strata, which are typical for river and floodplain deposits in this <br /> portion of the San Joaquin Valley (see Geologic Cross Section, Figure 2) While regional <br /> lateral and vertical variation are present in the aquifer and confining strata, these strata as <br /> a whole form the aquifer stratigraphy between about 10- to 24-feet The underlying <br /> confining strata display some lateral lithologic variations and were not observed to yield <br /> water However, given the lateral lithologic variation, and as mentioned above, it is <br /> possible that these strata leak (up or down) vertical gradients In our opinion, on the basis <br /> of these observations, both aquifer strata and the underlying confining strata are <br /> interpreted to have some lateral extent underlying the immediate site vicinity <br /> Chemical Analysis <br /> A total of thirty-nine (39) soil samples and eleven reconnaissance groundwater samples <br /> were analyzed at Chromalab, Inc a State certified analytical laboratory from the <br /> exploratory borings These samples were tested for the following, Total Petroleum <br /> Hydrocarbons as Gasoline (TPHG) and Diesel (TPHD), Benzene (B), Toluene (T), <br /> Ethylbenzene (E) and Xylene (X), Methyl-tert-butyl-ether (MTBE) and fuel oxygenates, <br /> using EPA Methods 3510/8015, 8020, 8240 and 8260 The results are tabulated and <br /> • presented in the attached Tables I and 2 below <br /> Discussion <br /> Soil Chemical Data <br /> The site assessment revealed that low concentrations of highly degraded contaminants <br /> were present in the capillary fringe at PB-17 (advanced through the edge of the former <br /> UST pit), at P13-15, 16 and 19 (immediately downgradient of the former UST pit) at PB- <br /> 10 and PB-18 near MW-9, and at PB-13 near MW-3 Other capillary fringe samples <br /> showed that contaminants were not detected Intermediate depth soil samples also <br /> showed that contaminants were not detected with the exception of PB-14-4 at 22 feet <br /> where 0 014 parts per billion (ppb) of Xylene were detected Contaminants were not <br /> detected in the deepest soil samples at PB-12-5 at 26 feet and PB-13-5 at 26 feet MTBE <br /> and oxygenates were not detected in any soil sample Soil samples collected at the 25-26 <br /> foot depths in PB-13, 18 and 19 showed that contaminants were not detected (see Tables <br /> 1 and 2) <br /> Reconnaissance Groundwater Chemical Data <br /> Four reconnaissance groundwater samples were collected on April 25, 2001, and all <br /> contained various concentrations of TPHG and BTEX contaminants (see Table 2) The <br /> highest concentrations observed from the April 25, 2000 bonngs were at PB-1 l (31,000 <br /> ppb TPHG and 170 ppb Benzene) and at PB-13 (21,000 ppb TPHG and 160 ppb <br /> . Benzene) MTBE and oxygenates were not detected in any groundwater sample (see <br /> Table 3) <br /> Page 6 <br />
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