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Musco Family Olive Company - 14 - 12 December 2006 <br /> and likely downgradient of this well. No other wells are located down-gradient to monitor water <br /> quality north-northeast of well MW-15. <br /> Well MW-16 <br /> Well MW-16 is below the Reservoir in the mid-gradient area. Like wells MW-13 through <br /> MW-15, TDS, chloride, and sodium are elevated either above the interim standards or <br /> Regional Well when compared. Although the trend plot suggests slightly variable or stable <br /> concentrations of chloride and sodium, the concentrations were elevated at the start of <br /> sampling. TDS concentrations show a sharp increase following the impoundment of <br /> wastewater in the Reservoir as shown in the Times Series plot. Initial TDS concentration was <br /> 2,300 mg/L in November 2002. TDS concentration measured in June 2006 was 2,700 mg/L. <br /> Well MW-16 is similar to well MW-15 where bicarbonate has significantly increased over time. <br /> The initial bicarbonate concentration was measured at 710 mg/L in November 2002. <br /> Bicarbonate was detected in well MW-16 at a concentration of 1,500 mg/L in June 2006. ' It is <br /> apparent from the time series plot the Reservoir is leaking wastewater containing elevated <br /> concentrations of bicarbonate and impacting down-gradient groundwater. <br /> Well MW-3 <br /> Well MW-3 is down-gradient of well MW-16 in the mid-slope area. TDS, chloride, and sodium <br /> concentrations exceed both the interim standards and the average concentrations detected in <br /> the Regional Well. As with the other wells discussed above, beginning concentrations of <br /> chloride and sodium are elevated but appear to be stable over time. However, like well <br /> MW-16, TDS and bicarbonate concentrations have been increasing as a result of groundwater <br /> impacts due to the leaking Reservoir. As with wells MW-15 and MW-16 there is no other <br /> apparent source of bicarbonate in groundwater that could be contributing to the elevated <br /> concentrations seen in well MW-3. <br /> Well MW-5 <br /> Well MW-5 is in the mid-slope area and like the other wells discussed above has elevated <br /> TDS, chloride, and sodium. Concentrations of these CDCs exceed both the interim standards <br /> and the average concentrations detected in the Regional Well. Well MW-5 is similar to wells <br /> MW-3 and MW-16 in that TDS and bicarbonate has been increasing over time. When <br /> reviewing the time series plot, TDS and bicarbonate has increased steadily following the <br /> impoundment of wastewater in the Reservoir. However, impacted groundwater in the vicinity <br /> of well MW-5 is also being affected by wastewater leaking from the 1-million gallon pond. Well <br /> MW-5 is located above the drainage swale but below the 1-million gallon pond, which provides <br /> a significant hydraulic head. As shown in Table 1, the 1-million gallon pond receives high <br /> strength wastewater that contains elevated concentrations of CDCs including bicarbonate. <br /> Wells MW-10, MW-11, and W-2 <br /> Wells MW-10, MW-11, and W-2 are dry wells. Consequently the limited data set was not <br /> graphed. However, upon review of the analytical results (Table 8) from each well for the last <br /> four available sampling events it is apparent that TDS, chloride, and sodium were detected at <br /> concentration levels above the interim standards and the Regional Well. Well MW-11 is <br />