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L �..� <br /> L January 24,2005 <br /> NOA Project Number: E04158A <br /> Methods 300.0 and 504.2,respectively. Nitrate was detected at a concentration of 17.1 mg/L-NO3i <br /> which is below the maximum contaminant level (MCL) of 45 mg/L-NO3 set by the California <br /> Department of Health Services. DBCP was not detected in the water sample. The laboartory <br /> analytical report sheets from Precision Enviro-Tech can be found in the appendix of this report. <br /> The presence of nitrates is not uncommon in shallow ground water aquifers in San Joaquin County <br /> and other parts of the Central Valley. Nitrate in ground water 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 ground water zones. <br /> 6. In the early 1900s,natural levels of nitrate in ground water were measured in forty-three (43)wells <br /> throughout the Sacramento Valley by Bryan (1923). It was thought that ground water at that time <br /> was close to"natural" conditions. Based on the work by Bryan,it is estimated that under"natural" <br /> conditions,ground water concentration containing nitrate is no more then about 13.5 mg/L-NO3 (3 <br /> mg/L-N). Areas having 24.75 mg/L-NO3 (5.5 mg/L-N) or more are those in which nitrate <br /> concentrations may be increasing(Hull, 1984). <br /> h DBCP is a nematocide and soil fumigant for vegetables and grapes. It is thought to cause health <br /> Lproblems consisting of kidney damage,liver damage,and cancer. The use of DBCP was <br /> discontinued in 1979.The Environmental Protection Agency (EPA) set the maximum contaminant <br /> i limit (MCL) at 0.2 parts per billion (ppb) because the EPA believes that given present technology <br /> yand resources,this is the lowest level to which water systems can reasonably be required to remove <br /> this contaminant should it occur in drinking water. <br /> 4.5 Well Water Sample Collection, Handling,and Transportation <br /> The exterior tap on the permanent residential structure was run wide-open for at least 10 minutes <br /> prior to collecting the water samples. The flow was then reduced and samples were collected directly <br /> into appropriate sample containers (one new plastic quart container,and one new 40 milliliter glass <br /> vial with HCL preservative). The samples were then transported on ice under proper chain of <br /> Lcustody to Precision Enviro-Tech, Stockton. <br /> L4.6 Chain of Custody <br /> Chain of Custody document for samples collected on is included in the appendix of this report. <br /> 5.0 SOIL PROFILE AND GEOLOGIC INFORMATION <br /> According to the Geologic Map of the San Francisco -San Jose Quadrangle, California(1991), the Site is <br /> Lunderlain by the Quaternary Riverbank Formation which is described as weathered reddish gravel, <br /> sand,and silt forming clearly recognizable alluvial terraces and fans (Plate 7). <br /> 1LThe surface and near surface soils located at the Site are reported by the to consist of the Madera <br /> 6 "04 <br /> u <br /> L <br />