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Impact of Biodiesel in Ozone Production in Atlanta

Impact of Biodiesel in Ozone Production in Atlanta. Siv Balachandran EAS 6410 4/24/07. Outline. Motivation Biodiesel Ozone Pollution Formation Overview of OZIPR Model Assumptions Model Results Conclusions. Motivation. Ozone is a primary pollutant under NAAQS

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Impact of Biodiesel in Ozone Production in Atlanta

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  1. Impact of Biodiesel in Ozone Production in Atlanta Siv Balachandran EAS 6410 4/24/07

  2. Outline • Motivation • Biodiesel • Ozone Pollution Formation • Overview of OZIPR Model • Assumptions • Model Results • Conclusions

  3. Motivation • Ozone is a primary pollutant under NAAQS • 8 hour standard: 0.08 ppm • 1 hour standard: 0.12 ppm • Only for certain areas • Altanta falls under this • Effects of ozone • Health (respiratory) • Damage to vegitation

  4. Ozone Trends in Atlanta http://www.grta.org/news_section/2005_Publications/2004_AQ_report_final.pdf

  5. Non-attainment Areas in Atlanta http://www.grta.org/news_section/2005_Publications/2004_AQ_report_final.pdf

  6. Recent Interest in Biofuels • Driven by several factors • Diesel emissions • Local self reliance • New markets for agricultural crops • Alternative Fuel Laws

  7. Biodiesel • Biodiesel = Tranesterifciation (Vegetable Oil) • Often catalyzed by acid or base • Byproducts • Glycerin, alcohol, catalyst en.wikipedia.org/wiki/Biodiesel, www.biodiesel.org

  8. Biodiesel Yields The Global Petroleum Club via en.wikipedia.org/wiki/Biodiesel

  9. Biodiesel Emission Impacts EPA Draft Technical Report: A Comprehensive Analysis of Biodiesel Impacts on Exhaust Emissions

  10. Ozone Pollution Formation • R1-R3: OH production • R4-R7: O3 production • R8-R9: sinks ftp://ftp.as.harvard.edu/pub/trop/publications/jacobbook/bookchap12.pdf

  11. Ozone Pollution Formation ftp://ftp.as.harvard.edu/pub/trop/publications/jacobbook/bookchap12.pdf

  12. OZIPR Model • 1-D photochemical box model • Trajectory model • Well mixed column of air from ground to mixed layer • Column moves with wind trajectory but cannot expand horizontally • 48 runs • 3 different meteorological conditions per season • Rural, Urban, Carbonyl, No Carbonyl http://www.epa.gov/scram001/dispersion_alt.htm#ozipr

  13. OZIPR Meteorological Conditions

  14. OZIPR Assumptions • Most basic level of OZIPR was used for this study • 8AM - 8PM analysis • Atlanta Summer Met. Condition 2 Urban with Carbonyl Emissions (ATLSU2UC) • OZIPR - unusually high default emissions • Emissions reduction percentages applied equally to each of the hourly emissions

  15. Emissions Assumptions • Only HDDV analyzed • Emission impacts from fuels • NREL study • Eastern USA • Net Reduction = (HDDV% of Mobile Emissions) x (Mobile% of Total Emissions) x (Emissions Reductions) • ULSD only reduced NOx emissions http://www.nrel.gov/vehiclesandfuels/npbf/pdfs/33793.pdf

  16. Model Results

  17. Model Results

  18. Discussion • B20, B100 and ULSD scenarios had little impact on O3 levels • Max 1 hour concentrations (ATLSU2UC): • No Biodiesel: 189.4 ppb • B20: 189.4 ppb • B100: 189.4 ppb • ULSD: 187.8 ppb • 50% NOx reduction: 174.2 ppb • 50% NOx reduction leads to 8.03% decrease in O3 • ULSD scenario - 0.08% decrease in O3

  19. Discussion • Max 1 hour concentrations (ATLSU1UC): • No Biodiesel: 152 ppb • B20: 152.1 ppb • B100: 152.3 ppb • ULSD: 149.5 ppb • 50% NOx reduction: 137.1 ppb • 50% NOx reduction leads to 9.80% decrease in O3 • ULSD scenario - 1.65% decrease in O3

  20. Discussion • Max 1 hour concentrations (ATLSU3UC): • No Biodiesel: 121.7 ppb • B20: 121.6 ppb • B100: 122 ppb • ULSD: 118.3 ppb • 50% NOx reduction: 101.7 ppb • 50% NOx reduction leads to 16.4% decrease in O3 • ULSD scenario - 2.79% decrease in O3

  21. Conclusions • Biodiesel use in HDDV doesn’t help in O3 reductions, but it doesn’t appear to hurt it • Other benefits • ULSD has more impact on O3 than B20 or B100 • NOx reduction is very important for O3 production Atlanta • Food vs. fuel

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