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ARCHIVED REPORTS_XR0004045
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PR0545387
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ARCHIVED REPORTS_XR0004045
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Last modified
3/5/2020 9:49:04 AM
Creation date
3/5/2020 8:24:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004045
RECORD_ID
PR0545387
PE
3528
FACILITY_ID
FA0005718
FACILITY_NAME
SINCLAIR TRUCKING
STREET_NUMBER
3780
Direction
W
STREET_NAME
LINNE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
3780 W LINNE RD
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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Geological TeckTics Inc. Page 3 <br /> Groundwater Monitoring Report <br /> Project No. 2030.2 <br /> October 22,2004 <br /> approximately 15-feet bgs. A clay layer dominates the site between 19 and 22 feet bgs. Each <br /> of the sites five water table wells terminated in "plastic" clay. Groundwater was encountered <br /> ' between 9.5-11.4 feet bgs. The capillary fringe extended approximately 4 feet above the <br /> water table. <br /> ' The deep well (MW-101) terminated in highly plastic "fat" clay. Dirty sand and clay define <br /> the 25-35 feet bgs lithology near the former USTs. The deep geology of the site is primarily <br /> poorly sorted sand with varying amounts of silt and clay. The screen interval of the deep well <br /> ' (MW-101) is located in dirty sand. MW-101 is the only deep well and defining the deep <br /> geology is limited to this data. <br /> ' 1.3.2 Groundwater Gradient and Bearing <br /> On July 14, 2004, the depth to groundwater was measured in all of the monitoring wells prior <br /> to purging. Depths to groundwater, at the site, averaged 8.91-feet below the top of casing <br /> (TOC). The average groundwater elevation for the April 2004 event was 67.56-feet above <br /> mean sea level (AMSL). Site-specific groundwater bearing and slope were calculated and <br /> ' found to be N40°E @ 0.0042 ft/ft. Groundwater elevation increased 2.45 feet since the April <br /> 2004 monitoring event. These results are consistent with average historical groundwater <br /> bearing and slope for this site. <br /> Vertical groundwater gradients were calculated for the site using the MW-1/MW-101 well <br /> pair and found to be positive. The site-specific vertical groundwater gradient is 0.0006 ft/ft. <br /> ' MW-1 is screened from 5 to 20.feet bgs and MW-101 is screened from 29.5 to 34.5 feet bgs. <br /> Vertical groundwater gradient calculations have been performed at regular intervals since the <br /> installation of MW-101 on April 12, 2002. The historical vertical gradients have typically <br /> ' been positive and approximately one order of magnitude less than the horizontal gradients. <br /> Groundwater elevation, bearing and slope were calculated using data gathered from MW-2, <br /> ' MW-3 and MW-4 during the July 14, 2004, monitoring event and the results are summarized <br /> in Table 1 of Appendix A. Table 2 of Appendix A summarizes the vertical groundwater <br /> gradient calculations. <br /> ' 1.3.3 Average Groundwater Velocity <br /> The lithology at the ST site will be divided into three general layers for the purposes of <br /> calculating the average horizontal groundwater velocity. Layer 1 consists of silts and clays <br /> from 5- to 15-feet bgs; Layer 2 is primarily sand with some fines from 15- to 20-feet bgs; <br /> Layer 3 is primarily clay from 20- to 25-feet bgs. The average depth to groundwater at the <br /> ' - site suggests groundwater flows horizontally through each of the four layers. ---- <br /> La.'s er 1 <br /> ' The average hydraulic conductivity (K), estimated from typical K values for silt and clay <br /> mixtures (Driscoll, 1986), 0.12 feet per year (ft/yr), and the average hydraulic gradient (i) <br /> across the site is approximately 0.0038. Based on the equation v = K i/n, where n is effective <br />
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