Journals / Atmospheric Pollution Research / 2017 / Cilt: 8 - Sayı: 2

A reduced form model for ozone based on two decades of CMAQ simulations for the continental United States

Pages
275–284
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

Emission-driven changes in monthly mean ozone levels for the period 2000e2010 ranged from 6.4 to 10.9 ppb for the eastern US and from 1.4 to 2.5 ppb for the western US.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:A Reduced Form Model (RFM) is a mathematical relationship between the inputs and outputs of an air quality model, permitting estimation of additional modeling without costly new regional-scale simulations.
📊
Key Findings & Data:A 21-year Community Multiscale Air Quality (CMAQ) simulation for the continental United States provided the basis for the RFM developed in this study.
💡
Conclusion & Impact:Emission-driven changes in monthly mean ozone levels for the period 2000e2010 ranged from 6.4 to 10.9 ppb for the eastern US and from 1.4 to 2.5 ppb for the western US.
🔬Design:Modeling & Simulation
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

A Reduced Form Model (RFM) is a mathematical relationship between the inputs and outputs of an air quality model, permitting estimation of additional modeling without costly new regional-scale simulations. A 21-year Community Multiscale Air Quality (CMAQ) simulation for the continental United States provided the basis for the RFM developed in this study. Predictors included the principal component scores (PCS) of emissions and meteorological variables, while the predictand was the monthly mean of daily maximum 8-h CMAQ ozone for the ozone season at each model grid. The PCS form an orthogonal basis for RFM inputs. A fewPCS incorporatemost of the variabilityof emissions and meteorology,thereby reducing the dimensionality of the source-receptor problem. Stochastic kriging was used to estimate the model. The RFM was used to separate the effects of emissions and meteorology on ozone concentrations. By running the RFM with emissions constant (ozone dependent on meteorology), or constant meteorology (ozone dependent on emissions). Years with ozone-conducive meteorology were identified, and meteorological variables best explaining meteorology-dependent ozone were identified. Meteorology accounted for 19%e55% of ozone variability in the eastern US, and 39%e92% in the western US. Temporal trends estimated for original CMAQ ozone data and emission-dependent ozone were mostly negative, but the confidence intervals for emission-dependent ozone aremuch narrower. Emission-driven changes in monthly mean ozone levels for the period 2000e2010 ranged from 6.4 to 10.9 ppb for the eastern US and from 1.4 to 2.5 ppb for the western US.

🔖

Cite This Article

PORTER, P. S., RAO, S., HOGREFE, C., MATHUR, R. (2017). A reduced form model for ozone based on two decades of CMAQ simulations for the continental United States. Atmospheric Pollution Research, Cilt: 8 - Sayı: 2, 275–284. https://ajindex.com/articles/216246

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (5)

  1. Xing, J., Pleim, J., Mathur, R., Pouliot, G., Hogrefe, C., Gan, C.-M., Wei, C., 2013. Historical gaseous and primaryaerosol emissions in the United States from 1990 to 2010. Atmos. Chem. Phys. 13, 7531e7549. http://dx.doi.org/10.5194/acp-137531-2013.
  2. Xing, J., Mathur, R., Pleim, J., Hogrefe, C., Gan, C.-M., Wong, D.C., Wei, C., Gilliam, R., Pouliot, G., March 2015. Observations and modeling of air quality trends over 1990e2010 across the Northern Hemisphere: China, the United States and Europe. Atmos. Chem. Phys. 15 (5), 2723e2747. http://dx.doi.org/10.5194/acp15-2723-2015.
  3. Wong, D.C., Pleim, J., Mathur, R., Binkowski, F., Otte,T., Gilliam, R., Pouliot,G., Xiu, A., Young, J.O., Kang, D., 2012. Geosci. Model Dev. 5, 299e312. http://dx.doi.org/ 10.5194/gmd-5-299-2012.
  4. Wold, S., Sjostrom, M., Eriksson, L., 2001. PLS‑regression: a basic tool of chemometrics. Chemom. and Intell. Lab. Syst. 58, 109e130. U.S. Environmental Protection Agency, 2006. Technical Support Document for the Proposed Mobile Source Air Toxics Rule: Ozone Modeling. Office of Air Quality Planning and Standards, Research Triangle Park, NC. U.S. Environmental Protection Agency. 2016. https://www.epa.gov/air-emissionsinventories/national-emissions-inventory, accessed March. TCEQ (Texas Commission on Envrionmental Quality). 2016. http://tceq.state.tx.us/ airquality/areasource/Sources_of_Air_Pollution.html/#Non-Road, accessed January 2016.
  5. Rao, S.T., Porter, P.S., Mobley, D., Hurley, F., November 2011. Understanding the Spatio-temporal variability in air pollution concentration. Environ. Manag. 42e48. Rao, S.T., Zurbenko, I.G., Neagu, R., Porter, P.S., Ku, J.U., Henry, R.F., 1997. Space and time scales in ambient ozone data. Bull. Am. Meteorol. Soc. 78, 2153e2166. Rao, S.T., Zurbenko, I.G., Porter, P.S., 1996. Dealing with the ozone non-attainment problem in the eastern United States. Environ. Manag. 1, 17e31. Porter, P.S., Rao, S.T., Hogrefe, C., Gego, E., Mathur, R., 2015. Methods for reducing biases and errors in regional photochemical model outputs for use in emission reduction and exposure assessments. Atmos. Environ. 112, 178e188. Porter, P.S., 2016. Ozone RFM for the Continental US: Model Inputs, Development and Performance. CRC Report No. A-89e2. Pavlovic, R., Chen, J., Anderson, K., Moran, M.D., Beaulieu, P.-A., Davignon, D., Cousineau, S., 2016. The FireWork air quality forecast system with near-realtime biomass burning emissions: recent developments and evaluation of performance for the