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SITE HISTORY_FILE 2
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3500 - Local Oversight Program
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PR0545273
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SITE HISTORY_FILE 2
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Last modified
2/3/2020 11:44:10 AM
Creation date
2/3/2020 11:02:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
FileName_PostFix
FILE 2
RECORD_ID
PR0545273
PE
3528
FACILITY_ID
FA0000174
FACILITY_NAME
JOES TRAVEL PLAZA
STREET_NUMBER
15600
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19620079
CURRENT_STATUS
02
SITE_LOCATION
15600 S HARLAN RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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3.2.2 Sand B Monitoring Wells <br /> Historically, in the Sand B monitoring wells (MW-8, MWO-1 x, MW-1413, and MW-15B), depth <br /> to water levels have been as shallow as 7.3 feet bgs to as deep as 12.4 feet bgs; the average depth <br /> to water over the historic monitoring period is 10.3 feet bgs. Seasonal fluctuations of water table <br /> levels beneath the site in the Sand B wells on the order of one to three feet per year are typical <br /> (Figure 6). Groundwater flow beneath the site, based on wells screened across the water table in <br /> Sand B, has been predominately northeast; however, in early 2006, a shift of the flow direction <br /> towards the north and northwest was observed. Water levels and fluctuations in Sand A and <br /> Sand B wells appear similar(Figure 6). <br /> 3.2.3 Sand C Monitoring Wells <br /> Historically, in the Sand C monitoring wells (MW-12C and MW-13C), depth to water levels <br /> have been as shallow as 11.4 feet bgs to as deep as 14.1 feet bgs; the average depth to water over <br /> the historic monitoring period is 12.9 feet bgs. Seasonal fluctuations of water table levels <br /> beneath the site in the Sand C wells of about two feet per year are typical (Figure 6). <br /> 3.2.4 Vertical Hydraulic Gradient <br /> To evaluate the component of vertical groundwater flow between the intervals of the saturated <br /> zone beneath the site in which groundwater monitoring wells have been constructed, <br /> �. groundwater elevations from the A/B well pairs MW-2/MWO-1 x, MW-9/MW-8, <br /> MW-14A/MW-14B, and MW-15A/MW-15B and B/C well pairs MW-8/MW-12C and <br /> MW-13A/B/MW-13C and were compared. During the periods in which the well pairs were <br /> gauged (27 quarters for MW-2/MWO-lx, 14 quarters for MW-9/MW-8, and 4 to 7 quarters for <br /> the remaining well pairs), differences in piezometric groundwater elevations ranging from—0.67 <br /> to +0.22 feet (or about 2.5 to 8 inches) were measured at the A/B well cluster locations <br /> indicating relatively small upward and downward components of flow between the A/B <br /> intervals. The lack of consistent differences in potentiometric head elevations between wells <br /> may suggest no dominant vertical groundwater flow between the A/B portions of the saturated <br /> zone. At the B/C cluster well locations, differences in piezometric groundwater elevations <br /> ranging from —0.50 to —2.11 feet were measured at the B/C well cluster locations indicating a <br /> consistent downward component of flow between the B/C intervals. <br /> 3.3 Extent of Petroleum and Fuel-Oxygenate Hydrocarbon Impact <br /> 3.3.1 Soil <br /> Since the initiation of environmental assessment work at the site in January 1997 through March <br /> 2007, more than one hundred soil samples at depths up to 73 feet bgs were collected and <br /> analyzed to evaluate the presence and distribution of fuel-related hydrocarbons and oxygenates <br /> in soil surrounding the two main source areas (the northern and southern former USTs) (Table <br /> 2). Analytical results of these samples indicate that chemicals of concern (COCs) for the site in <br /> Page 12 5TKA WO <br />
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