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ARCHIVED REPORTS_2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
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ARCHIVED REPORTS_2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
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Last modified
2/10/2020 6:58:46 PM
Creation date
2/10/2020 4:41:37 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
RECORD_ID
PR0542464
PE
2960
FACILITY_ID
FA0024404
FACILITY_NAME
CHEVRON FUEL TERMINAL 1001621
STREET_NUMBER
22888
STREET_NAME
KASSON
STREET_TYPE
RD
City
BANTA
Zip
95304
APN
23906015, 16, 17
CURRENT_STATUS
01
SITE_LOCATION
22888 KASSON RD
P_LOCATION
03
QC Status
Approved
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S E C O R <br /> • 2003 Feasibility Study Report and Site Assessment Work Plan <br /> July 18, 2003 <br /> Page 3 <br /> the B zone encountered as shallow as 50 feet bgs (SECOR, 2003b). The lower boundary of the B- <br /> zone has not been explored. <br /> 2.2.1 Groundwater Flow Rates, Directions, Recharge, and Discharge <br /> A 2003 Aquifer Testing Report, (SECOR, 2003d) suggests hydrogeologic communication exists <br /> between the Upper A zone and A zone onsite. However, locally, there is no distinction between the <br /> Upper A and A zones. Groundwater beneath the site generally flows to the north with gradients <br /> ranging from approximately 0.0008 feet per foot (ft/ft) to 0.06 ft/ft. A rose diagram showing the <br /> historical gradient and flow directions of shallow groundwater (i.e. Upper A and A zones) is provided <br /> as Figure 5 (SECOR, 2003c). <br /> Aquifer test results indicate an average transmissivity(T) and specific yield (Sy) of approximately 381 <br /> square feet per day (ft 2/day) and 0.41 cubic feet per cubic feet (ft3 per ft), respectively. Based on a <br /> saturated thickness of 20 feet in the A zone, the average conductivity (K) was approximately 19 feet <br /> per day (ft/day) or 0.0067 centimeters per second (cm/sec). The pumping well radius of influence <br /> (ROI) was calculated to be approximately 83 feet. <br /> Historical groundwater gradient data suggests that shallow groundwater flows toward and may <br /> discharge to Tom Paine Slough and the Paradise Cut. Groundwater in the area appears to <br /> recharge from rain fall. The average rain fall for the city of Tracy is 7.9 inches annually <br /> (hftp://www.worldclimate.com/cgi-bin/data.pl?ref=N37Wl 21+2200+048996C). <br /> • 2.2.2 Groundwater Use <br /> The San Joaquin groundwater basin underlies the site. Beneficial uses of groundwater in the area <br /> include municipal, irrigation, stock watering, process and service supply (SECOR. 4'h Quarter <br /> /Annual 2002 Quarterly Groundwater Monitoring Report). <br /> A summary of water wells within a one mile radius of the site and their approximate locations are <br /> provided as Table 1 and Figure 6, respectively. There are no county or city operated pumping wells <br /> in the general area. San Joaquin County municipal water supply wells are typically screened in the <br /> Lower Tulare Aquifer. <br /> Groundwater located in the Upper A, A and B zone beneath the site is not used for human <br /> consumption due to naturally poor water quality. In a conversation between SECOR and Lee Helms <br /> (Helms, Lee. Telephone Interview. 13 May 2003), Mr. Helms indicated a domestic well on his <br /> property produces water high in total dissolved solids (TDS), and this water is not used for human <br /> consumption . <br /> 2.2.3 Extraction Wells Affect on Groundwater Flow <br /> One onsite groundwater extraction well (WSW-1) and fourteen offsite groundwater extraction wells <br /> were identified within a one mile radius of the site (Table 1 and Figure 6). Based on historical <br /> groundwater monitoring data, pumping from these wells does not appear to impact groundwater flow. <br /> No groundwater injection wells were identified in the vicinity of the site. <br /> I:\Chevron\1001621\REPORTS\2003\2003FS\FS_.2003_revD.doc <br />
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