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Published byEthelbert Welch Modified over 8 years ago
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THE FALSE POSITIVE CONUNDRUM: IDENTIFYING FALSE POSITIVES OF CONTAMINATION FROM LANDFILLS IN SEMI-ARID TO ARID WESTERN WATERSHEDS Maxwell Gade Graduate Student Syracuse University Dr. Donald Siegel Professor, Earth Science Syracuse University
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Wyoming Department of Environmental Quality, 2010
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Wind River Formation
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Valley Fill
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Baedecker and Back, 1979 Landfill contamination has a unique fingerprint
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Major Reactions Organic matter oxidation Carbonate mineral dissolution Ion exchange Sulfate reduction Iron oxide reduction Ammonium generation under anoxia
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Landfill Leachate Indicators Alkalinity Sodium Chloride Absence of Sulfate Dissolved Organic Carbon
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As an assemblage natural variability is very large and has no logical trends
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Highest Possible Concentration
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Maximum Possible Orders of Magnitude Higher Orders of Magnitude Higher Plausible Total Iron is not thermodynamically reasonable Total metal analyses cause false positives
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Wyoming Department of Environmental Quality, 2010
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Sand Draw Case Study
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Water levels in wells have not varied in years
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Figure 4 Sodium-sulfate Water
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Water isotopes Fall on Completely Different Line than Modern Water Siegel, 2009
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Some Water is Thousands of Years Old WellDepth (ft)C-14 AgeC-13 R-1050 R-1150 R-12504550-21.0 R-185217180-7.7 R-20553650-19.3 R-750 R-850 R-9D6022130-10.8 R-13D9029-16.7 R-19D19120-14.6 R-216600-17.3 Wash well~2006020-11.1
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Sand Draw Sample Comparison
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Conclusions The chemistry in ground waters contaminated with leachate must be consistent with landfill geochemical processes The local variability of constituents needs to be assessed in a hydrological context To avoid false positives samples should be filtered, using only dissolved constituent values
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