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ARCHIVED REPORTS_XR0012638
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0528359
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ARCHIVED REPORTS_XR0012638
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Last modified
5/8/2020 3:58:19 PM
Creation date
5/8/2020 2:53:22 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012638
RECORD_ID
PR0528359
PE
2950
FACILITY_ID
FA0019146
FACILITY_NAME
SHELL OIL PRODUCTS US
STREET_NUMBER
3725
Direction
N
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95304
APN
21217030
CURRENT_STATUS
02
SITE_LOCATION
3725 N TRACY BLVD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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r <br /> v <br /> x� <br /> it <br /> IN <br /> t�a3F�ssap arrF assE93M£N� REPORT <br /> Shull O{1 Company <br /> 3725 TrwC Boulevard,?racy,Call[ornia <br /> r< W Delta Proj-t No.4o-89-012 <br /> ,Page 7 <br /> Cross-section A-A' traverses from the northwest to the wtitheast corner of the site through <br /> monitoring well MW-3,soil borings SB-4 and SB-3,and monitoring well MW-2(Figure 2). Cross- <br /> section A-A' is shown in Figure 3. The sites underlain by sandy to silty clay and clayey silt to a <br /> depth of 12 to 15 feet. Underlying the finer grained soils are silty sands which were observed to a <br /> depth of 21 feet below the ground surface. <br /> 1.7 f3raund Watgl: <br /> Depths to ground water were measured and recorded in the monitoring wells on September 26 and <br /> October 13, 1989. Ground water was observed between 9 and 11 feet below the ground surface.. Al! <br /> field measurements and observations are presented in Table 2. The direction of ground water flow <br /> was calculated using the ground water elevations on September 26 and October 13, 1989. The <br /> i direction of ground water flow on September 26, 1989,before ground water samples were collected <br /> was from the south to the north at a gradient of 0.001 foot/foot. A ground water contour map was <br /> . The direction of ground water flow on October 13, 1989, <br /> generated `inti is presented in Figure 4 <br /> was from the southeast to the northwest at a gradient of 0.001 faotJfaot. <br /> TABLE 2 <br /> l'-•-- Ground Water Level Data <br /> Depth to <br /> j= Reference Ground Water Ground Water Physical <br /> E1 va ' (feet)- fes{below r v i Observations <br /> 9.45 88.00 No odor <br /> t� MW-1 09-26-89 97.45 9.22 88.23 No odor <br /> 10-13-89 <br /> 9.31 88.14 No odor <br /> MW-2 09-26-89 97.45 9.18 88.27 No odor <br /> 10-13-89 <br /> 88.02 No odor <br /> MW-3 09-26-89 99.17 11.15 rvo odor <br /> 10-13-89 <br /> 11.00 88.17 <br /> l 1,;.l Hydraulic Conductivil.Y <br /> -bearing materials were estimated by performing slug tests on <br /> Hydraulic conductivity of the water <br /> - - -- --- - the three_monitoring wells(mW-1, MW-2,and MW-3), and by grain size analysis of soil samples <br /> collected from soil boring SB-8 at depths of 16 and 20 feet within she water bearing matedr- e - <br /> with methods presented in Bower and Rice, 1976. The <br /> slug test data were evaluated in accordance <br /> grain size data were analyzed using equations developed by Hazen (Freeze and Cherry, 1977, and <br /> Krumbeun and Monk, 1943). Analysis of the slug test data indicated hydraulic conductivity for the <br /> sandy to clayey silts, which were observed at the water table, averaged l8 fee[ per day(Table 3). <br />
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