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DRAFT Mobile sensitivity How sensitive is the air quality model to changes in VMT?

DRAFT Mobile sensitivity How sensitive is the air quality model to changes in VMT?. Mike Abraczinskas, Laura Boothe, George Bridgers, Phyllis Jones, Vicki Chandler, Ming Xie, Wyat Appel NC Division of Air Quality Attainment Planning Branch September 30, 2004. Objective.

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DRAFT Mobile sensitivity How sensitive is the air quality model to changes in VMT?

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  1. DRAFTMobile sensitivityHow sensitive is the air quality model to changes in VMT? Mike Abraczinskas, Laura Boothe, George Bridgers, Phyllis Jones, Vicki Chandler, Ming Xie, Wyat Appel NC Division of Air Quality Attainment Planning Branch September 30, 2004

  2. Objective • Show how the air quality model (ozone) responds to changes in VMT • Changes relative to “current” emissions • Changes relative to “future” emissions • In this study • Current = 2000 • Future = 2007 • Modeling System and Episode • MM5, SMOKE, CMAQ modeling system • June 12-15, 1997 (4 day episode)

  3. Background • 2002 VMT were submitted to VISTAS for base case modeling • In select counties where no TDM VMT was provided, but where TDM data will be available in the future… a “factored” universe file VMT number was used • The “factor” – a 30% increase – was based on past differences showing that TDM VMT is usually about 30% higher than VMT from the NCDOT universe file.

  4. Domain Reductions/increases were applied to counties in Red

  5. Current year sensitivities • 2 sensitivity runs were completed to provide some indication on how predicted ozone concentrations would change if current year VMT estimates were off by 10%. • Current year (w/ a 10% reduction in VMT) • Current year (w/ a 10% increase in VMT)

  6. Test 1 10 % reduction in VMT relative to “current” year (2000)

  7. 10 % reduction in VMT relative to “current” year (2000) Ozone

  8. 10 % reduction in VMT relative to “current” year (2000) Ozone

  9. 10 % reduction in VMT relative to “current” year (2000) Ozone

  10. 10 % reduction in VMT relative to “current” year (2000) Ozone

  11. 10 % reduction in VMT relative to “current” year (2000)Impacts on ozone DVFs • 6 of 36 NCDAQ monitoring sites experienced changes in DVFs (a rigorous application of the USEPA attainment test across the 4-days modeled, 4 km domain only) • Recall: DVF = RRF*DVC RRF = future/current • In this sensitivity, only the denominator of the RRF changes • Monitor CountyDelta DVF (ppb) • Rockwell Rowan 1 ppb • Duke St Durham 1 ppb • Sophia Randolph 1 ppb • Farmville Pitt 1 ppb • Wade Cumberland 1 ppb • Taylorsville Alexander 1 ppb

  12. 10 % reduction in VMT relative to “current” year (2000) DVF Change < 1 ppb

  13. Test 2 10 % increase in VMT relative to “current” year (2000)

  14. 10 % increase in VMT relative to “current” year (2000) Ozone

  15. 10 % increase in VMT relative to “current” year (2000) Ozone

  16. 10 % increase in VMT relative to “current” year (2000) Ozone

  17. 10 % increase in VMT relative to “current” year (2000) Ozone

  18. 10 % increase in VMT relative to “current” year (2000)Impacts on ozone DVFs • 10 of 36 NCDAQ monitoring sites experienced changes in DVFs (a rigorous application of the USEPA attainment test across the 4-days modeled, 4 km domain only) DVF Change < 1 ppb DVF Change > 1 ppb

  19. Future year sensitivities 2 sensitivity runs were completed to provide some indication on how predicted ozone concentrations would change if future year VMT estimates were off by 20%. • Future year (w/ a 20% reduction in VMT) • Future year (w/ a 20% increase in VMT)

  20. Test 3 20 % decrease in VMT relative to “future” year (2007)

  21. 20 % decrease in VMT relative to “future” year (2007) Ozone

  22. 20 % decrease in VMT relative to “future” year (2007) Ozone

  23. 20 % decrease in VMT relative to “future” year (2007) Ozone

  24. 20 % decrease in VMT relative to “future” year (2007) Ozone

  25. 20 % decrease in VMT relative to “future” year (2007)Impacts on ozone DVFs • 16 of 36 NCDAQ monitoring sites experienced changes in DVFs (a rigorous application of the USEPA attainment test across the 4-days modeled, 4 km domain only) • Recall: DVF = RRF*DVC RRF = future/current • In this sensitivity, only the numerator of the RRF changes 2 locations showed an ozone DVF change of 2 ppb 14 locations showed an ozone DVF change of 1 ppb

  26. Test 4 20 % increase in VMT relative to “future” year (2007)

  27. 20 % increase in VMT relative to “future” year (2007)Impacts on ozone DVFs • 16 of 36 NCDAQ monitoring sites experienced changes in DVFs (a rigorous application of the USEPA attainment test across the 4-days modeled, 4 km domain only) • Recall: DVF = RRF*DVC RRF = future/current • In this sensitivity, only the numerator of the RRF changes 5 locations showed an ozone DVF change of 2 ppb 11 locations showed an ozone DVF change of 1 ppb

  28. Caveats • Thorough QA is not complete • Only 4 days were analyzed • Additional days may alter the preliminary conclusions • Significance of impact will depend on predicted future ozone • Additional analysis is needed

  29. Preliminary Conclusions • VMT changes of +/- 10% in the current year modeling will have a minor impact on ozone future design values • VMT changes of +/- 20% in the future year modeling will have more of an impact on ozone future design values

  30. Preliminary Conclusions • Additional investigations could include: • Generation of additional metrics • frequency of changes • daily RRF changes • Additional episodes to include a greater variety of meteorological conditions • Additional days may alter the conclusions • Additional analysis is needed.

  31. Questions/Comments http://ncair.org Michael.Abraczinskas@ncmail.net 919-715-3743

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