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Cemex Vema6s Cluarry Mining and Reclamation Project <br /> v <br /> Cystalline silica is analyzed in the revised air quality analysis utilizing the HARP model (see <br /> Appendix A).The health risk from crystalline silica exposure,with standard dust control <br /> measures,is found to be less than significant. <br /> Response to Comment B-58 <br /> Commenter states that the air dispersion modeling used to analyze impacts to public health <br /> through the estimate of ambient concentrations of toxic air contaminants in inadequate, as it <br /> relied on five years of meteorological data from the Fresno Airport. These airport data are <br /> neither site-specific nor is the quality of this data set acceptable for air dispersion modeling. <br /> Commenter speculates that the public health risk assessment which relies on these data for air <br /> modeling is flawed and likely underestimates modeled concentrations and thus health risk. <br /> Commenter states that the Applicant should be required to collect one year ofpre-construction — <br /> meteorological data, the risk assessments and other analyses that rely on dispersion modeling <br /> should be revised, and the Draft EIR recirculated far review. <br /> The Fresno Airport data represents the best available information. The Fresno data set,was <br /> determined to have the most similar air-land characteristics,per CARB's California Surface Wind <br /> Climatology. The suggestion that one year of pre-construction data should be collected prior to <br /> preparation of a Draft EIR does not meet the "reasonableness"test for a CEQA analysis for a <br /> project of this type. <br /> Response to Comment B-59 <br /> Commenter states that the cumulative impacts needs to include the proposed Valley Rock Mine. <br /> A cumulative CEQA analysis can be done in one of two ways per CEQA Guidelines Section <br /> 15130(6).The first is a list of past,present, and probable future projects. The second is to use <br /> projections in an adopted planning document. The air quality cumulative analysis is based on the <br /> air quality plans described on page 4.6-8. The SJVAPCD considers any criteria pollutant that <br /> would have a direct impact to also have a cumulative impact. In addition, PM emissions were <br /> found to be cumulatively significant in the DEIR(see DEIR Chapter 6). <br /> Response to Comment B-60 <br /> Commenter states the statements regarding the cumulative Project air quality impacts ofNOx, <br /> ROG, PM10, PM2.5, and DPM are conclusory and unsupported. Commenter also states that the <br /> Draft EIR should be revised to evaluate the cumulative impacts of construction impacts, odor <br /> impacts, and public health impacts from the asphalt plant operation and other facilities. <br /> See Response to Comment B-59 regarding cumulative impacts. Odor impacts were analyzed in <br /> Impact 4.6.3. Public health impacts from the asphalt plant were analyzed in Impact 4.6.7 and <br /> were reassessed using the HARP model in the revised air quality analysis,attached to this FEIR <br /> as Appendix A. Also see the response to comment B-12 regarding PM2.5 and Draft EIR pages <br /> 4.6-4 and 4.15 for more information. <br /> Cem Vernslm Quarry Mming aM Reclamation Prmea 3-22 ESA 1203015 <br /> Final Environmental Impact Report June 2008 <br />