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.Mann-Kendall test, is a nonparametric, rank correlation method which can be used for <br /> evaluating correlations between constituent concentrations and time. The test is described <br /> in statistical literature (Gilbert, 1987; hollander and Wolfe, 1973) and its use is <br /> recommended by the U.S. EPA (Loftin, et al., 1989). As stated previously in Section 6.3, <br /> the effectiveness of the capping of the landfill may not be observable for several years. The <br /> concentration limit for MW-5 will be no increasing trends. <br /> Inorganic Parameters. As described in the Article S Monitoring Program (EMCON, <br /> 1992), natural spatial variations in groundwater quality have been identified at the Corral <br /> Hollow Sanitary Landfill. Where spatial variations exist, it is inappropriate to designate a <br /> single upgradient well (or group of wells) as background because it may not encompass <br /> the range of naturally occurring constituent concentrations present at a site. Instead, each <br /> well should function as its own background. Therefore, concentration limits for the <br /> downgradient wells MW-4 and SB-1 will be calculated based on background water quality <br /> data using the tolerance interval method. <br /> The tolerance method was approved for use at the Corral Hollow Sanitary Landfill by <br /> WDR Order No. 94-259. This statistical method is described in literature (Montgomery, <br /> 1985) and in the Article S Monitoring Program (EMCON, 1992). Tolerance limits for the <br /> Corral Hollow Sanitary Landfill will be updated on a quarterly basis to provide ongoing <br /> definition of water quality for the landfill, as required by WDR Order No. 94-259. <br /> Concentration limits for MW-4, as calculated for the first quarter 1995, are shown on <br /> Table 2. Concentration limits for SB-1 will be established after sufficient data have been <br /> collected <br /> For the impacted well MW-5, during corrective action monitoring, inorganic parameters <br /> will be evaluated for decreasing trends (and increasing trends in the cases of <br /> nitrate-nitrogen and pH) to evaluate the effectiveness of the CAP. Consistent with this <br /> evaluation procedure, the concentration limits for inorganic constituents will be "the <br /> absence of a statistically significant increasing trend." <br /> One exception is nitrate-nitrogen; its depletion in groundwater can be used as an indicator <br /> of ongoing landfill impact. Under the anaerobic conditions that are encountered within <br /> landfills,facultative microorganisms will use nitrate as an electron acceptor, thus depleting <br /> nitrate concentrations. Therefore, a decreasing trend in nitrate-nitrogen concentrations <br /> would be indicative of continuing landfill impact. Conversely, increasing nitrate-nitrogen <br /> concentrations can be used to indicate the effectiveness of corrective action activities. The <br /> concentration limit for nitrate-nitrogen is therefore "the absence of a statistically <br /> significant decreasing trend." A second exception is pH, for which both an increasing and <br /> a decreasing trend would be indicative of landfill impact. The concentration limit for pH is <br /> "the absence of both an increasing and a decreasing trend." <br /> SAC\N.\PJ0M3M390031.9BG-94Wb:1 <br /> Rev.0,4121/95 <br /> 0939-003.19 7-2 <br />