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Nitrate Loading study Irerracon <br /> Cho Property a Ripon,California <br /> September n, 2048 ■ Terracon Project No. NAI 87038 <br /> 2.2 Potential Ground Water Contamination issues <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 /> "naturae" conditions, groundwater concentration containing nitrate is no more than about 13.8 <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(dibromochloropropane) is a nematicide and soil fumigant for vegetables and grapes. It is <br /> thought to cause health problems consisting of kidney damage, liver damage, and cancer. The <br /> use of DBCP was discontinued in 1979. EDB (ethylene dibromide) was used in gasoline to <br /> prevent lead deposits and build up. It was also used in pesticides and fumigants. Exposure to <br /> EDB is linked to many adverse health effects stemming from organ damage to cancer. <br /> Agricultural land use and septic systems in the area should be considered potential groundwater <br /> contamination sources. The concerns for groundwater contamination in this area are deemed <br /> moderate to high based on the agricultural land use and anticipated depth to groundwater <br /> between 45 to 60 feet bgs. <br /> 2.3 Current and Future On-Site Ground Water Uses <br /> According to Mr. Cho, there are no groundwater wells located on the site. fir. Cho indicated the <br /> site will be developed with a groundwater supply well for future residential use. Based on the <br /> absence of an onsite groundwater well, a groundwater sample was not collected. <br /> 3.0 SOURCES AND WFACT OF NITRATE TO GROUNDWATER <br /> 3.1 Current Off-Site Sources of Nitrate <br /> The adjoining properties consist of agricultural land primarily orchards and rural farm structures <br /> and/or residences. Terracon assumes the farm structures and/or residences are connected to <br /> individual septic systems based on the absence of municipal sewer systems in the area as <br /> reported on the San Joaquin County District Viewer. Therefore, off-site sources of nitrate include <br /> residential septic systems, agricultural land use, and natural processes. <br /> Based on information obtained from the DWR Water Data Library, between the years 1959 to <br /> 2012, dissolved nitrate was reported between 5 and 70.4 rng/L-N at three groundwater wells <br /> located within one mile north and northeast of the site. A groundwater study titied Addressing <br /> Responsive ■ Resourceful ■ Reliable 5 <br />