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2900 - Site Mitigation Program
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PR0528324
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Last modified
2/6/2020 2:49:33 PM
Creation date
2/6/2020 9:12:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0528324
PE
2965
FACILITY_ID
FA0019131
FACILITY_NAME
SUTTER HOME LODI WINERY
STREET_NUMBER
18667
STREET_NAME
JACOB BRACK
STREET_TYPE
RD
City
LODI
Zip
95242
APN
01109014
CURRENT_STATUS
01
SITE_LOCATION
18667 JACOB BRACK RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Kennedy/Jenks Consultants <br /> In many of the soil borings, the upper 8 to 9 feet consisted of silty sand, and in borings KB-4 and <br /> KB-6 the entire 10 feet of the boring consisted of silty or well-graded sand. The clay and silt P <br /> soils logged in the soil borings were very stiff to stiff and typically had low to no plasticity. <br /> Although some soils were very stiff to stiff, no cemented 'hardpans' were observed. The soil rr <br /> boring logs and analytical results were included in the ROWD (Kennedy/Jenks 2008). <br /> 2.3.2 Hydrogeology <br /> Generally, the subsurface consists of a mixture of silty or clayey layers, although well-graded <br /> i <br /> sand was reported in the boring for GW-6 and poorly-graded sand in the borings for GW-9, <br /> GWA0, GWA1, GWA2, GWA5, and GWA8. I <br /> In the soil borings, the first-encountered groundwater was typically observed at the base of the <br /> silty sand just above a deeper clay or silt layer. Groundwater was also observed in the clay and <br /> silt layers if sand was absent. The stabilized groundwater levels in the wells indicate that the j <br /> shallow aquifer is unconfined. <br /> 2.3.2.1 Groundwater Gradient it <br /> Groundwater monitoring data indicate that the groundwater flow direction at the facility is <br /> generally from east to west. The highest groundwater levels are typically measured in January <br /> or February. February 2013 groundwater elevations on the east side of the site ranged from <br /> 5.48 feet above Mean Sea Level (MSL) at GWA to 6.58 feet above MSL at GWA7, while those <br /> on the west side ranged from 3.59 feet above MSL at GW-14 to 3.87 feet above MSL at GW-6. <br /> The groundwater elevations presented in the monitoring reports are measured relative to <br /> Condor Control Point No. 1. The survey report included in Condor(2002) indicates this control <br /> T <br /> point is at elevation 14.48 but does not provide the datum. Subsequent Condor monitoring <br /> reports state that groundwater elevations are referenced to a "relative datum", probably <br /> meaning Condor Control Point No. 1. � <br /> The groundwater gradient magnitude based on the elevations referenced to the relative datum <br /> is typically around 0.0005 feet per foot. The small gradient magnitude is a function of the <br /> proximity to the Delta and the flat local topography. 1 <br /> 2.3.2.2 Facility Groundwater Quality <br /> Condor has monitored the groundwater quality at the facility on behalf of Sutter Home <br /> since 2002. The analytical results for TDS from a recent groundwater sampling event involving <br /> onsite wells (February 2013) are summarized in Table 3. The TDS concentration data indicate <br /> some variability which is difficult to attribute to specific activities. However, these TDS j <br /> concentrations are also consistent with those measured in wells throughout the region. <br /> 2.4 Water Supply <br /> Source water for facility operations is supplied by a groundwater supply well located at the <br /> eastern side of the site. The supply well provides water for both domestic and process uses. A ;a <br /> well log for the supply well was not available but the well was reportedly drilled to 225 feet bgs, <br /> installed with 16-inch diameter casing and 30 feet of screen at the bottom of the well. <br /> al <br /> Page 6 Monitoring Well Installation Work Plan e <br /> Sutter Home Winery, Lodi, California <br /> O!i.*.d .'gobOW6500513 swerhvmeNWep�4 ,MWw Ada <br />
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