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5.1 AIR QUALITY <br /> • Results of the ambient air quality modeling analyses <br /> • PSD increment consumption <br /> 5.1.5.2 Model Selection <br /> The screening and refined air quality impact analyses were performed using the American <br /> Meteorological Society/Environmental Protection Agency Regulatory Model Improvement <br /> Committee (AERMIC) model,also known as AERMOD (current version 04300). The <br /> AERMOD model is a steady-state,multiple-source,Gaussian dispersion model designed for <br /> use with stack emission sources situated in terrain where ground elevations can exceed the <br /> stack heights of the emission sources (i.e. complex terrain).9 The model is capable of <br /> estimating concentrations for a wide range of averaging times (from 1 hour to 1 year). <br /> Inputs required by the AERMOD model include the following: <br /> • Model options <br /> • Meteorological data <br /> • Source data <br /> • Receptor data <br /> Model options refer to user selections that account for conditions specific to the area being <br /> modeled or to the emissions source that needs to be examined. Examples of model options <br /> include use of site-specific vertical profiles of wind speed and temperature;consideration of <br /> stack and building wake effects; and time-dependent exponential decay of pollutants. The <br /> model supplies recommended default options for the user for some of these parameters. <br /> AERMOD uses hourly meteorological data to characterize plume dispersion. The <br /> representativeness of the data is dependent on the proximity of the meteorological monitoring <br /> site to the area under consideration,the complexity of the terrain,the exposure of the <br /> meteorological monitoring site,and the period of time during which the data are collected.The <br /> meteorological data used in this analysis were collected at the Woodley Island NWS. <br /> 5.1.5.3 Good Engineering Practice Stack Height Analysis <br /> For the purposes of modeling, a stack height beyond what is required by Good Engineering <br /> Practices (GEP) is not allowed (40 CFR Part 60 §51.164). However,this requirement does not <br /> place a limit on the actual constructed height of a stack.GEP as used in modeling analyses is <br /> the height necessary to ensure that emissions from the stack do not result in excessive <br /> concentrations of any air pollutant in the immediate vicinity of the source as a result of <br /> atmospheric downwash,eddies, or wakes that may be created by the source itself,nearby <br /> structures,or nearby terrain obstacles. In addition,the GEP stack height modeling restriction <br /> assures that any required regulatory control measure is not compromised by the effect of that <br /> portion of the stack that exceeds the GEP height. The EPA guidance ("Guideline for <br /> Determination of Good Engineering Practice Stack Height," Revised 6/85) for determining <br /> GEP stack height indicates that GEP is the lesser of 65 meters or Hg,where Hg is calculated as <br /> follows: <br /> Hg= H + 1.5L <br /> 9 AERMOD was adopted in November 2005 as a guideline model by EPA as a replacement for ISCST3.AERMOD incorporates <br /> an improved downwash algorithm as compared to ISCST3(Federal Register,November 9,2005;Volume 70, Number 216, <br /> Pages 68218-68261). <br /> 5.1-34 SAC/371322/082410013(LEC_5.1_AIR_QUALITY.DOC) <br />