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Soil Suitability Study Irerracon <br /> Flag City#4 Lodi, California <br /> February 14, 2019 Terracon Project No. NA187043 <br /> Water Resources (DWR) Water Data Library, between the years 1989 and 2013, depth to <br /> groundwater measured between approximately 14 to 28 feet bgs at a groundwater well located <br /> approximately one quarter mile south of the site. <br /> Based on a review of the Lines of Equal Elevation of Groundwater maps available on the <br /> SJCFCWCD website, between 2015 and 2016 groundwater flow appeared to have a southerly <br /> direction; however, the groundwater flow direction and the depth to shallow, unconfined <br /> groundwater, if present, would likely vary depending upon seasonal variations in rainfall and other <br /> hydrogeological features.Without the benefit of on-site groundwater monitoring wells surveyed to <br /> a datum, groundwater depth and flow direction beneath the site cannot be directly ascertained. <br /> 4,2 Potential Groundwater Contamination Issues <br /> Identifying potential groundwater contamination sources was not part of the scope of work for the <br /> SSS. Potential groundwater contamination can occur from a number of sources including <br /> historical petroleum hyrdrocarbon use, agricultural activities, dairies, septic systems, and storm <br /> water infiltration. As per EHD requirements nitrate as N and 1,2-dibromo-3-chloropropane <br /> (DBCP) have been included as part of the SSS discussion. <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 /> mg/L-NO3 (3 mg/L-N). Areas having 24.75 mg/L-NO3 (5.5 mg/L-N) or more are those in which <br /> nitrate concentrations may be increasing (Hull, 1984). <br /> DBCP is a nematicide and soil fumigant for vegetables and grapes. It is thought to cause health <br /> problems consisting of kidney damage, liver damage, and cancer. The use of DBCP was <br /> discontinued in 1979. <br /> Based on the historical information, agricultural land use and septic systems in the area should <br /> be considered potential groundwater contamination sources. Refer to Section 4.4 for further <br /> discussion. <br /> 4,3 Water Sample Location <br /> One groundwater well is currently located on the northern portion of the site. It is our <br /> understanding the groundwater well is intended to be used for the proposed development. Refer <br /> to Section 4.4 for further discussion. <br /> Responsive ■ Resourceful ■ Reliable 7 <br />