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Human and Ecological Risk Assessment - Earthjustice

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Appendix BWaste Management UnitsFor l<strong>and</strong>fills, because the data were limited (8 sites), the model runs assumed that thepercent below grade ranged from 1 to 100 <strong>and</strong> was uniformly distributed. For each l<strong>and</strong>filliteration, a r<strong>and</strong>om value for percent below grade was picked <strong>and</strong> applied to the l<strong>and</strong>fill depth todetermine depth below ground surface. This value was constrained to be no deeper than thewater table <strong>and</strong> was checked to see that EPACMTP groundwater mounding constraints were notviolated.For surface impoundments, more data were available (16 sites), with 8 sites beingconstructed entirely below grade <strong>and</strong> the remaining 8 sites ranging from 7.5 to 45 feet abovegrade. For each surface impoundment iteration, height above grade at these 15 sites wasr<strong>and</strong>omly sampled as an empirical distribution <strong>and</strong> applied to the overall surface impoundmentdepth to determine depth below ground surface.B.6 Calculation of WMU Depth <strong>and</strong> Imputation of Missing WMU DataThe EPRI survey includes information on the total area <strong>and</strong> total waste capacity of eachl<strong>and</strong>fill <strong>and</strong> surface impoundment included in the survey. To calculate average depth for eachWMU (a necessary EPACMTP model input), the total waste capacity was divided by the area.The resulting depths were then checked for reasonableness. For surface impoundments, onedepth (1 foot) was culled as being unrealistically low <strong>and</strong> one (700 feet) as too high. Two l<strong>and</strong>filldepths less than 2 feet <strong>and</strong> one depth greater than 350 feet were also removed from the database.In these cases the EPRI waste capacity data were culled <strong>and</strong> replaced using the regressionsdescribed below (i.e., WMU areas are considered more reliable than the capacity estimates in thesurvey data), <strong>and</strong> new capacities were estimated as described below.In addition, four l<strong>and</strong>fills <strong>and</strong> six surface impoundments had neither area nor capacitydata in the EPRI survey. In these cases, the EIA facility locations were used to find the plants<strong>and</strong> their WMUs on aerial photos from the Terraserver Web site (http://terraserver-usa.com/geographic.aspx), <strong>and</strong> a geographic information system (GIS) was used to measure the areas ofthe units in question. Capacities were then estimated as described below.To impute data for facilities missing either area or capacity data in the EPRI survey,linear regression equations were developed based on WMUs with both area <strong>and</strong> capacity data,one to predict area from capacity, <strong>and</strong> one to predict capacity from area. The final regressionequations are shown in Figures B-4 <strong>and</strong> B-5 for l<strong>and</strong>fills <strong>and</strong> Figures B-6 <strong>and</strong> B-7 for surfaceimpoundments. In each case, a st<strong>and</strong>ard deviation around the regression line was also computed<strong>and</strong> used during source data file preparation to r<strong>and</strong>omly vary the area or capacity from iterationto iteration within the bounds of the existing data set.April 2010–Draft EPA document. B-7

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