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drop was typically from sixth to at least thirteenth or more. Four of the nine compounds dropped <br />from the ranking and rank no more than 17`x. The average MSW landfill contribution per <br />compound dropped from 13% to 1.5%: One of the more dramatic findings concerns U.S. EPA's <br />original attribution of 84% of all 1,1,2,2 -Tetrachloroethane emissions to landfills; the WIAC <br />findings show that the landfill emission level is about 2% of all sources. These findings indicate <br />that municipal landfills have markedly less emissions, compared to other industrial sources, than <br />U.S. EPA previously estimated. <br />Table 3. Summary of changes to Urban Air Toxic (UAT) emission estimates based on changes from <br />AR42 defaults to current compound levels measured by WIAC. <br />Portion of UAT Number <br />Annual Tons Inventory Rank of <br />Comnound AP42 I WIAC I AP -42 I WIAC AP -42 I WIAC Sources <br />I <br />1'1'2'2 <br />216 <br />1.0 <br />84.08% <br />2.37% <br />1 <br />5 <br />16 <br />compounds, the differences were larger yet. The overestimated AP -42 values may potentially <br />Tetrachloroethane <br />misdirect U.S. EPA's policy development. For example, the recently completed Urban Air Toxics <br />Strategy appears to have substantially overestimated actual landfill emissions. Furthermore, the <br />existing AP -42 default values may adversely impact individual landfills required to use these <br />values. <br />As a result, WIAC believes that the AP -42 defaults should be revised to reflect the decline in <br />23.6 <br />3.0 <br />3.59% <br />1.48% <br />6 <br />8 <br />12 <br />Dichloropropane <br />Acrylonitrile <br />389 <br />2.2 <br />.15.28% <br />0.10% <br />3 <br />15 <br />17 <br />Benzene <br />173 <br />87.9 <br />3.86% <br />2.00% <br />11 <br />13 <br />17 <br />Chloroform <br />4.17 <br />1.3 <br />4.94% <br />1.63% <br />6 <br />9 <br />17 <br />Ethylene Dichloride <br />47 <br />13.7 <br />1.15% <br />0.34% <br />10 <br />* <br />17 <br />Methylene Chloride <br />1550 <br />367 <br />1.67% <br />0.40% <br />11 <br />* <br />17 <br />Tetrachloroethylene <br />717 <br />229 <br />0.59% <br />0.19% <br />6 <br />* - <br />17 <br />Trichloroethylene <br />429 <br />104 <br />0.64% <br />0.16% <br />13 <br />* <br />17 <br />Vinyl Chloride <br />531 <br />77.9 <br />19:65% <br />3.46% <br />2 <br />4 <br />17 <br />Vinylidene <br />22:5. <br />10.3 <br />1010% <br />3.45% <br />4 <br />5 <br />14 <br />Chloride <br />Landfill emissions are <br />less than for other ranked sources. <br />I <br />Conclusions <br />WIAC conducted a national survey of recent LFG analyses. Recent results from 75 landfills were <br />analyzed using AP -42 methodologies. The AP -42 defaults were found to typically overestimate <br />current levels by two to four hundred percent. For some of the more health.significant <br />compounds, the differences were larger yet. The overestimated AP -42 values may potentially <br />misdirect U.S. EPA's policy development. For example, the recently completed Urban Air Toxics <br />Strategy appears to have substantially overestimated actual landfill emissions. Furthermore, the <br />existing AP -42 default values may adversely impact individual landfills required to use these <br />values. <br />As a result, WIAC believes that the AP -42 defaults should be revised to reflect the decline in <br />LFG constituents. The most recent AP -42 revision in 1995 added new data to older values and <br />averaged the combined data sets. This approach is appropriate only for data that does not trend. It <br />is recommended that older data be purged and replaced using current data presented in this paper. <br />I <br />