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ARCHIVED REPORTS XR0013118
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0515454
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ARCHIVED REPORTS XR0013118
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Entry Properties
Last modified
11/19/2024 10:19:10 AM
Creation date
12/14/2018 4:56:34 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0013118
RECORD_ID
PR0515454
PE
2960
FACILITY_ID
FA0012157
FACILITY_NAME
POMBO REAL ESTATE
STREET_NUMBER
1755
Direction
W
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
23217020
CURRENT_STATUS
01
SITE_LOCATION
1755 W ELEVENTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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/>0Q:= <br /> GEOMAWIM <br /> plastic end caps,and tape. Soil samples were labeled,sealed in plastic bags,and stored in an ice- <br /> cooled chest <br /> Grab groundwater samples were collected from borings GMX-25,GMX-27,GMX-29 through <br /> GMX-31, and GMX-33. To collect grab groundwater samples from the borings,a temporary well <br /> was constructed of 1-inch diameter Schedule 40 polyvinyl chloride(PVC)piping consisting of blank <br /> casing and a 5-foot-long slotted well screen with 0.01-inch slots. The PVC well screen and blank- <br /> casing were lowered into the drive casing and the drive casing then was retracted three to four feet <br /> from the bottom of the boring to expose the water-bearing material while maintaining a surface seal. <br /> A small-diameter baler was then lowered into the PVC piping and groundwater was decanted from <br /> the bailer into laboratory-supplied sample containers. Sample containers were labeled,sealed in <br /> plastic bags,and stored in an ice-cooled chest. <br /> The soil and grab groundwater samples were submitted to Friedman and Bruya,Inc.,of Seattle, <br /> Washington,a Califomia-certified analytical laboratory,under Geomamx chamof-custody <br /> procedures. Soil samples were submitted for analysis for TPHc(Go-Cm carbon range)using EPA <br /> Method 8015 Modified;PAHs using EPA Method 8270 SIM;and BTEX using EPA Method 8020. <br /> Grab groundwater samples were analyzed for TPHg (C6 to C12 carbon range)and TPHd(CIO to C24 <br /> carbon range)using EPA Method 8015 Modified;BTEX using EPA Method 8021B;and PAHs <br /> using EPA Method 8270 SIM. TPHd analyses were performed both with and without a silica gel <br /> preparation procedure to assess the presence of polar biodegradation byproducts in the groundwater <br /> samples. An aliquot of the sample from GMX-29(located within affected soil)was filtered by the <br /> laboratory with a 0.7-micron glass fiber filter prior to extraction and analysis to assess the presence of <br /> non-dissolved constituents adhered to particulates in the sample. Because the sample was collected <br /> within affected soil and it contained significant particulates,such interference from non-dissolved <br /> constituents was expected. <br /> Following collection of the soil and grab groundwater samples,the boreholes were backfilled with <br /> cement grout placed from the total depth of the boring to ground surface with a treme pipe. <br /> 5.0 ANALYTICAL RESULTS <br /> Soil sample analytical results are summarized in Table 3 and are presented on Figure 2. <br /> No TPHc,BTEX,or PAHs were detected in soil samples from GMX-25,GMX-27,GMX-30, <br /> GMX-31,or GMX-33. TPHc was detected in soil samples collected from GMX-26 and GMX-32 at <br /> concentrations of 120 and 1,700 mg/kg,respectively. BTEX were not detected in either of these <br /> \\SF3\DEPTDATA\D0C SAFE\6000SNW7.003\P0ME0S0IL6W RPTNOV00 .DOC 5 <br />
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