Uncertainties influencing dynamic evaluation of ozone trends

Slides:



Advertisements
Similar presentations
Heather Simon, Adam Reff, Benjamin Wells, Neil Frank Office of Air Quality Planning and Standards, US EPA Ozone Trends Across the United States over a.
Advertisements

NASA AQAST 6th Biannual Meeting January 15-17, 2014 Heather Simon Changes in Spatial and Temporal Ozone Patterns Resulting from Emissions Reductions: Implications.
Quantifying CMAQ Simulation Uncertainties of Particulate Matter in the Presence of Uncertain Emissions Rates Wenxian Zhang, Marcus Trail, Alexandra Tsimpidi,
1 icfi.com | 1 HIGH-RESOLUTION AIR QUALITY MODELING OF NEW YORK CITY TO ASSESS THE EFFECTS OF CHANGES IN FUELS FOR BOILERS AND POWER GENERATION 13 th Annual.
OTAG Air Quality Analysis Workgroup Volume I: EXECUTIVE SUMMARY Dave Guinnup and Bob Collom, Workgroup co-chair “Telling the ozone story with data”
Using Air Quality Models for Emissions Management Decisions
1 Asheville Air Quality Megan Stone. 2 Clean Smokestacks Act Passed in 2002 by the General Assembly of North Carolina Passed in 2002 by the General Assembly.
Observation-constrained probabilistic evaluation of modeled concentrations and sensitivities Daniel Cohan and Antara Digar CMAS Conference October 16,
Did the recession impact recent decreases in observed sulfate concentrations? Shao-Hang Chu, US EPA/OAQPS/AQAD October, 2011.
EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS.
The Impact of Biogenic VOC Emissions on Tropospheric Ozone Formation in the Mid-Atlantic Region Michelle L. Bell Yale University Hugh Ellis Johns Hopkins.
1 Summary of LADCO’s Regional Modeling in the Eastern U.S.: Preliminary Results April 27, 2009 MWAQC TAC June 15, 2009.
Georgia Environmental Protection Division Uncertainty Analysis of Ozone Formation and Emission Control Responses using High-order Sensitivities Di Tian,
INCORPORATING UNCERTAINTY INTO AIR QUALITY MODELING & PLANNING – A CASE STUDY FOR GEORGIA 7 th Annual CMAS Conference 6-8 th October, 2008 Antara Digar,
Photo image area measures 2” H x 6.93” W and can be masked by a collage strip of one, two or three images. The photo image area is located 3.19” from left.
UNCERTAINTIES INFLUENCING HEALTH-BASED PRIORITIZATION OF OZONE ABATEMENT OPTIONS UNCERTAINTIES INFLUENCING HEALTH-BASED PRIORITIZATION OF OZONE ABATEMENT.
On the Model’s Ability to Capture Key Measures Relevant to Air Quality Policies through Analysis of Multi-Year O 3 Observations and CMAQ Simulations Daiwen.
Preliminary Study: Direct and Emission-Induced Effects of Global Climate Change on Regional Ozone and Fine Particulate Matter K. Manomaiphiboon 1 *, A.
1 Emission and Air Quality Trends Review Central States May 2013.
CMAQ APPLICATION TO OZONE POLLUTION IN THE PEARL RIVER DELTA OF CHINA Wei Zhou 1,2,Yuanghang Zhang 1,Xuesong Wang 1,Daniel Cohan 2 1.College of Environmental.
2012 CMAS meeting Yunsoo Choi, Assistant Professor Department of Earth and Atmospheric Sciences, University of Houston NOAA Air quality forecasting and.
Deguillaume L., Beekmann M., Menut L., Derognat C.
Climate Change and Ozone Air Quality: Applications of a Coupled GCM/MM5/CMAQ Modeling System C. Hogrefe 1, J. Biswas 1, K. Civerolo 2, J.-Y. Ku 2, B. Lynn.
C. Hogrefe 1,2, W. Hao 2, E.E. Zalewsky 2, J.-Y. Ku 2, B. Lynn 3, C. Rosenzweig 4, M. Schultz 5, S. Rast 6, M. Newchurch 7, L. Wang 7, P.L. Kinney 8, and.
Effects of Emission Adjustments on Peak Ground-Level Ozone Concentration in Southeast Texas Jerry Lin, Thomas Ho, Hsing-wei Chu, Heng Yang, Santosh Chandru,
1. How is model predicted O3 sensitive to day type emission variability and morning Planetary Boundary Layer rise? Hypothesis 2.
Chemical Condition and Surface Ozone in Urban Cities of Texas During the Last Decade: Observational Evidence from OMI, CAMS, and Model Analysis Yunsoo.
Diagnosing the sensitivity of O 3 air quality to climate change over the United States Moeko Yoshitomi Daniel J. Jacob, Loretta.
May 22, UNDERSTANDING THE EFFECTIVENESS OF PRECURSOR REDUCTIONS IN LOWERING 8-HOUR OZONE CONCENTRATIONS Steve Reynolds Charles Blanchard Envair 12.
Robert W. Pinder, Alice B. Gilliland, Robert C. Gilliam, K. Wyat Appel Atmospheric Modeling Division, NOAA Air Resources Laboratory, in partnership with.
Evaluation of CMAQ Driven by Downscaled Historical Meteorological Fields Karl Seltzer 1, Chris Nolte 2, Tanya Spero 2, Wyat Appel 2, Jia Xing 2 14th Annual.
1 Emission and Air Quality Trends Review Idaho July 2013.
Impact of Temporal Fluctuations in Power Plant Emissions on Air Quality Forecasts Prakash Doraiswamy 1, Christian Hogrefe 1,2, Eric Zalewsky 2, Winston.
Emission reductions needed to meet proposed ozone standard and their effect on particulate matter Daniel Cohan and Beata Czader Department of Civil and.
Response of fine particles to the reduction of precursor emissions in Yangtze River Delta (YRD), China Juan Li 1, Joshua S. Fu 1, Yang Gao 1, Yun-Fat Lam.
Accuracy of multi-parameter response surfaces generated from sensitivity coefficients Daniel Cohan and Antara Digar CMAS Conference 2009 October 19, 2009.
1 Emission and Air Quality Trends Review Northeastern States July 2013.
Applicability of CMAQ-DDM to source apportionment and control strategy development Daniel Cohan Georgia Institute of Technology 2004 Models-3 Users’ Workshop.
Yuqiang Zhang1, Owen R, Cooper2,3, J. Jason West1
Emission and Air Quality Trends Review
Dynamic Evaluation of CMAQ-Modeled Ozone Response to Emission Changes in The South coast air Basin Prakash Karamchandani1, Ralph Morris1, Andrew Wentland1,
Meteorological drivers of surface ozone biases in the Southeast US
Stephen Reid, Hilary Hafner, Yuan Du Sonoma Technology, Inc.
The 96th AMS Annual Meeting
Photochemical Modeling of Industrial Flare Plumes with SCICHEM 3.1
Source Apportionment Modeling to Investigate Background, Regional, and Local Contributions to Ozone Concentrations in Denver, Phoenix, Detroit, and Atlanta.
Byeong-Uk Kim and Jim Boylan Planning and Support Program
Taras Shevchenko University, Kiev, Ukraine
Emission and Air Quality Trends Review
17th Annual CMAS Conference, Chapel Hill, NC
Emission and Air Quality Trends Review
Sensitivity Analysis of Ozone in the Southeast
Emission and Air Quality Trends Review
Impact of NOx Emissions in Georgia on Annual PM2.5
Emission and Air Quality Trends Review
The relationship between summertime ozone peak hour and NOx and VOC emissions Jianfeng Li April 21, 2016.
J. Burke1, K. Wesson2, W. Appel1, A. Vette1, R. Williams1
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Topic 3: Meteorology and data filtering
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Diagnostic and Operational Evaluation of 2002 and 2005 Estimated 8-hr Ozone to Support Model Attainment Demonstrations Kirk Baker Donna Kenski Lake Michigan.
Emission and Air Quality Trends Review
Updating a Fuel-based Inventory of Vehicle Emissions
Emission and Air Quality Trends Review
Presentation transcript:

Uncertainties influencing dynamic evaluation of ozone trends Wei Zhou and Daniel Cohan Rice University 10th Annual CMAS Conference October 26, 2011

Emission reduction leads to the improvement of air quality US EPA,2010

Objectives Evaluate the performance of air quality model in modeling air quality trend - identify the direction and magnitude of trend - characterize the spatial feature Investigate the impact of uncertain parameters on modeling O3 trend - Meteorology - Emission estimate and trend - Chemical reactions

Modeling summer ozone change from 2002 to 2006 Substantial emission reduction and O3 decrease Consistent modeling systems for both years Observational data for modeling evaluation

Emission trend from 2002 to 2006 Year Elevated emission (ktons) Ground emission Total 2002 1324 2193 3517 2006 930 2012 2942 Difference(2006-2002) -29.8% -8.3% -16.3% Elevated emission: Electrical Generating Units (EGUs) and Non-EGUs Ground emission: mobile, non-road, and other sources Elevated emission: greater reduction and relatively low uncertainty Ground emission: less reduction and higher uncertainty

Metrics to evaluate ozone change Difference of concentration (DIF) = C(2006)-C(2002) -Negative: downward trend -Positive: upward trend 95th percentile of cumulatively distributed 8hr O3 concentration Daily maximum 8hr O3 averaged over the episode

Comparison of NOx change between model and observation DIF_OBS_NOx DIF_NOx(ppb) DIF_MOD_NOx

Comparison of O3 change between model and observation DIF_O3(ppb) DIF_OBS_O3 DIF_MOD_O3

No clear correlation between ozone trend and temperature variability DIF_TEMP= daily maximum temperature in 2006- daily maximum temperature in 2002

Evaluating modeled NOx and O3 trend in large urban areas

Improvement of modeled O3 trend by adjusting NOx emission NOx Adjustment factor= 1-OBS_NOx/MOD_NOx Atlanta Chicago Houston New York Pittsburgh Philadelphia 2002 0.14 -0.09 -0.3 -0.26 0.3 -0.05 2006 0.20 -0.20 -0.28 -0.11

Uncertain parameters affecting the simulation of O3 trend NOx emission - emission estimate - emission reduction trend VOC emission Chemical reaction - photolysis rates - reaction rate (e.g. OH+NO2->HNO3)

Perturbing uncertain parameters to improve the simulation of O3 trend Decrease NOx estimate Increase NOx reduction trend Decrease VOC emission Increase photolysis rates Decrease the reaction rate of OH+NO2-> HNO3

Conclusion Model generally captures the direction of O3 change but significantly underestimates the magnitude of O3 decrease Adjusting NOx emission improves the modeling of O3 downward trend but the O3 decreases remain underestimated Modeled O3 trend can be modestly improved by perturbing uncertainty in NOx emission and trend, VOC emission, photolysis and chemical reactions

Acknowledgement National Science Foundation CAREER Award #0847386 Sergey Napelenok of US EPA US EPA Air Quality System(AQS)