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Soil Suitability/ Nitrate Loading Study Irerracon <br /> Souza Property Tracy, CA <br /> February 28, 2020 Terracon Project No. NA207011 <br /> The maximum daily flow rate for the existing residence is 560 gpd and the proposed residence is <br /> 420 gpd for a combined total of 980 gpd. <br /> 1.4 Groundwater Information <br /> 1.4.1 Groundwater Depth and Gradient <br /> Groundwater was not encountered within our borings which were drilled between 3 and 10.0 feet <br /> below ground surface (bgs). <br /> According to the California Department of Water Resources, Groundwater Information Center <br /> Interactive Map, in 2018, depth to groundwater was reported between approximately 110 and 120 <br /> feet bgs in the Spring and between approximately 120 and 130 feet in the Fall. Based on a review <br /> of the San Joaquin County Flood Control and Water Conservation District Groundwater Report, <br /> Lines of Equal Depth to Groundwater Spring and Fall 2015 to 2016, depth to groundwater was <br /> reported between approximately70 to 80 feet. Based on a review of the sources, depth to <br /> groundwater is anticipated to be greater than 80 feet bgs. <br /> The groundwater flow direction and the depth to shallow, unconfined groundwater, if present, <br /> would likely vary depending upon seasonal variations in rainfall and other hydrogeological <br /> features. Without the benefit of on-site groundwater monitoring wells surveyed to a datum, <br /> groundwater depth and flow 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 /> Responsive ■ Resourceful ■ Reliable 7 <br />