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Appendix G <br />Air Quality Analysis Modeling Report <br />4.4 Emission Sources and Modeled Emission Rates (Far-Field Analysis) <br />Emission sources modeled in CALPUFF-Cite were established similarly to those modeled in <br />AERMOD, as described in Section 3.4 of this Report. All emission sources and activities are the <br />same, and the project is divided into three distinct phases (railroad construction, mine <br />area/transmission line/haul road construction, and production), with distinct timelines for each <br />project phase. However, rather than establishing all emission sources as area sources in the <br />model, the transmission line, railroad, and haul roads were characterized as volume sources in <br />CALPUFF-Cite. Table 4-2 provides a summary of the emission sources included in each phase <br />of the far-field analysis. <br />Table 4-2 <br />SUMMARY OF EMISSION SOURCES INCLUDED IN FAR-FIELD <br />ANALYSIS, BY PROJECT PHASE <br /> Phase 2 <br /> Phase 1 <br />Construction: Mine Area / Phase 3 <br />r <br />Emission Source Railroad Production <br /> Transmission Line /Haul <br /> Construction Roads <br />Volume 1: Transmission Line X <br />Volume 2: Railroad X <br />Volume 3: Haul Roads X <br />Area: Mine Area X X <br />1Mine area emissions during production phase include emissions from vehicle traffic on mine area roads. <br />The transmission line, railroad, and haul road emission sources used in the far-field (CALPUFF- <br />Lite) analysis are not "bounded," as they were in the near-field (AERMOD) analysis. The full <br />extent of the proposed transmission line, railroad, and haul road (14.5, 14.5, and 4.6 miles, <br />respectively) are included in the CALPUFF-Cite-defined emission sources. Refer to Figure 3-1 <br />for an illustration of these emission sources, but note that Figure 3-1 does not show the full <br />extent of these emission sources as represented in CALPUFF-Cite. Detailed source parameters <br />used in the far-field analysis are provided in Table 4-3. <br />G-21 <br />DBMS 533 <br />