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Soil Suitability/ Nitrate Loading Study Irerracon <br /> Jeremy Winery ■ Lodi, CA <br /> May 7, 2019 ■ Terracon Project No. NA197008 <br /> 1.4 Groundwater Information <br /> 1.4.1 Groundwater Depth and Gradient <br /> Groundwater was not encountered within our geotechnical or percolation test borings which were <br /> excavated between 3.5 feet below grade surface (bgs) and 25 feet bgs. <br /> According to the San Joaquin County Flood Control and Water Conservation District Groundwater <br /> Report (SJCWCD) Lines of Equal Depth to Groundwater Spring and Fall 2015 to 2016, <br /> groundwater depth lies between approximately 120 and 130 feet bgs. Based on a review of <br /> Department of Water Resources (DWR) Well Completion Report dated 2015 for the adjoining <br /> northern property, depth of the static water level measured at 90 feet bgs. The groundwater flow <br /> direction and the depth to shallow, unconfined groundwater, if present, would likely vary <br /> depending upon seasonal variations in rainfall and other hydrogeological features. Without the <br /> benefit of on-site groundwater monitoring wells surveyed to a datum, groundwater depth and flow <br /> direction beneath the site cannot be directly ascertained. <br /> 1.4.2 Potential Groundwater Contamination Issues <br /> Potential groundwater contamination can occur from a number of sources including historical <br /> petroleum hydrocarbon use, agricultural activities, dairies, septic systems, and storm water <br /> infiltration. As per EHD requirements nitrate as N and 1,2-dibromo-3-chloropropane (DBCP) have <br /> been included as part of the SSS discussion. Identifying potential groundwater contamination <br /> other than nitrates and DBCP is beyond the scope of work for this report. <br /> The presence of nitrates is not uncommon in shallow groundwater aquifers in San Joaquin County <br /> and other parts of the Central Valley. Nitrate in groundwater occurs as a result of the application <br /> of fertilizers, livestock waste, and untreated septic tank waste. Nitrate is mobile and often <br /> accumulates in the shallow groundwater zones. <br /> In the early 1900s, natural levels of nitrate in groundwater were measured in forty-three (43)wells <br /> throughout the Sacramento Valley by Kirk Bryan (1923). It was thought that groundwater at that <br /> time was close to "natural" conditions. Based on the work by Bryan, it is estimated that under <br /> "natural" conditions, groundwater concentration containing nitrate is no more than about 13.5 <br /> milligrams per liter (mg/L) nitrate (NO3) or (3 mg/L-N). Areas having 24.75 mg/L-NO3 (5.5 mg/L- <br /> N) or more are those in which nitrate concentrations may be increasing (Hull, 1984). <br /> DBCP (dibromochloropropane) is a nematocide and soil fumigant for vegetables and grapes. It <br /> is thought to cause health problems consisting of kidney damage, liver damage, and cancer. The <br /> use of DBCP was discontinued in 1979. <br /> Based on a review of the DWR Water Data Library, from the 1950s to 1970s a groundwater well <br /> station depicted approximately 0.25 miles west of the site, was analyzed for various constituents <br /> Responsive ■ Resourceful ■ Reliable 7 <br />