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r- <br /> • 7 <br /> k <br /> anions varied with aquifer depth. The shallow ground water appeared to be of a <br /> bicarbonate/chloride quality, such as shown by the Hall well analyses (Figure 13), while deep <br /> ground water appeared to be of a bicarbonate/sulfate quality as shown by the Brown's New well <br /> analyses (Collins, 1928; Piper, 1953; Hem, 1959) (Figure 14). <br /> I , <br /> A notable apparent increase (25 to 35 percent) in bicarbonate (and alkalinity) concentration was <br /> observed in samples from all the network wells during the October 1995 and January 1996 <br /> monitoring periods (see Figures 13 and 14). Upon discussion with laboratory staff, (K. <br /> Wilkinson, Fruit Growers Lab, personal communication, March 1996), it was their opinion that a <br /> calibration problem accounted for a portion of this apparent increase. As can be seen in Figures <br /> 13 and 14 and in Table 2, the bicarbonate (and alkalinity) concentration from each subsequent <br /> sampling period has "returned" to the lower concentration observed during the initial year and <br /> one-half of monitoring. The results from May 1996 were confirmed by an independent <br /> laboratory (Table 2). Thus, it appears that the apparent increase in bicarbonate concentration, <br /> during October 1995 and January 1996 was largely due to laboratory error, with some small <br /> portion resulting from actual seasonal or annual fluctuations of ground-water general mineral <br /> quality. To date, Teichert Aggregates has not yet commenced aggregate mining, thus eliminating <br /> the possibility'that an actual increase occurred due to Teichert's mining activities (L. Noble, <br /> Teichert Aggregates, personal communication, February 7, 1997). A more detailed analysis of <br /> the apparent increase has been provided previously (LSCE, 1996). <br /> -water constituents, nitrate levels were elevated in both shallow <br /> In regard to other notable ground <br /> and deep well samples; with concentrations in the South Tracy 41 production well fluctuating <br /> slightly above and below the drinking water maximum contaminant level (MCL) of 45 mg/l <br /> during the last three years. The lowest nitrate concentrations have typically been observed in <br /> samples from the Brown's wells. It should be noted that a gradual increase in nitrate <br /> concentration has been observed in the Hall well, from 15 to 31 mg/l over the past three years <br /> (Table 2) (Figure 15). These elevated nitrate concentrations appear to be indicative of historical <br /> agricultural land use in the area and, as mentioned above, cannot be due to aggregate mining. <br /> E <br /> © LUHDUFiFF & SCALMANINI <br /> CONS L3 LTIN G GN GI NFF RE <br /> jC' <br />