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Human and Ecological Risk Assessment - Earthjustice

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Appendix CSite DataAppendix C. Site DataThe site characteristics used in this analysis were based on site-specific, regional, <strong>and</strong>national data sources to provide the environmental parameters necessary for modeling the fate<strong>and</strong> transport of coal combustion waste (CCW) constituents released in l<strong>and</strong>fill or surfaceimpoundment leachate. Site-specific data were collected for the area in the immediate vicinity ofthe waste management unit (WMU), <strong>and</strong> included the geographic relationship among importantfeatures such as the WMU boundary, residential well location, <strong>and</strong> streams <strong>and</strong> lakes. These datawere collected at each of the 181 coal-fired power plants selected for the analysis. These 181locations across the continental United States were intended to represent the geographicdistribution of onsite WMUs used for disposal of CCW <strong>and</strong> were used to capture nationalvariability in meteorology, soils, climate, aquifers, <strong>and</strong> surface waterbodies at the disposal sites.C.1 Data Collection MethodologyThe CCW risk assessment employed site-specific, regional, <strong>and</strong> national data. Sitespecificdata were collected around CCW plant locations from the Energy InformationAdministration (EIA) database to obtain data for each facility that were representative of theenvironment immediately surrounding the plant. When site-specific data were not available,regional or national scale data sources were used. Where appropriate, distributions were used inthe Monte Carlo analysis to capture site-to-site, within-site, <strong>and</strong> national variability in theparameters collected.Data were collected around each CCW site using a geographic information system (GIS)that allowed (1) site-specific data to be assembled from the area immediately surrounding thefacility <strong>and</strong> (2) the site to be assigned to a region to collect regional data. To account forlocational uncertainty for the CCW WMUs 1 , a 5-km radius was used to define the data collectionarea for aquifer type <strong>and</strong> soil data. If multiple soil or aquifer types occurred within this radius,multiple types were sent to the model, weighted by the fraction of the collection area that theyoccupied. Surface waterbody type <strong>and</strong> stream flows also were collected for each site byidentifying the nearest stream segment.Climate <strong>and</strong> water quality data were collected by assigning each site to a HydrologicEvaluation of L<strong>and</strong>fill Performance (HELP) model climate station <strong>and</strong> a U.S. Geological Survey(USGS) hydrologic region. The EPA STOrage <strong>and</strong> RETrieval (STORET) database was used asthe source for water quality data, with parameters selected from distributions queried from thisdatabase for each region.Because the EIA locations were not exact for the WMUs being modeled, a nationaldistribution of stream distances was developed by manually measuring the distance between the1 The EIA latitudes <strong>and</strong> longitudes usually represent a facility centroid or front-gate location for each power plant.Because these facilities are often large, the WMUs are frequently located some distance from the plant itself <strong>and</strong>not at the EIA location.April 2010–Draft EPA document. C-1

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