The effect of emission control measures on ozone concentration

Slides:



Advertisements
Similar presentations
Cost estimate and control effective of multi-pollutant abatement from the power sector in the Yangtze River Delta region, China Jian Sun and Joshua S.
Advertisements

NASA AQAST 6th Biannual Meeting January 15-17, 2014 Heather Simon Changes in Spatial and Temporal Ozone Patterns Resulting from Emissions Reductions: Implications.
Li ZHANG, Hong LIAO, and Jianping LI Institute of Atmospheric Physics Chinese Academy of Sciences Impacts of Asian Summer Monsoon on Seasonal and Interannual.
University of Leicester CityZen Contributions
1 Surface O 3 over Beijing: Constraints from New Surface Observations Yuxuan Wang, Mike B. McElroy, J. William Munger School of Engineering and Applied.
Development, evaluation, and application of GEOS-Chem driven by CCSM3 meteorological fields Presenter: Daeok (Daniel) Youn Atmospheric Chemistry Modeling.
Hong Liao Institute of Atmospheric Physics Chinese Academy of Sciences Simulation of Air Pollutants (AP) over China using the GEOS-CHEM.
Better Air Quality in Asian and Pacific Rim Cities (BAQ 2002) December 2002, Hong Kong SAR The Trend of Acid Rain in China W. Wang 1,3, T. Wang 2,
Geophysical Fluid Dynamics Laboratory Review June 30 - July 2, 2009 Geophysical Fluid Dynamics Laboratory Review June 30 - July 2, 2009.
INTERCONTINENTAL TRANSPORT OF AIR POLLUTION WITH GMI AND PLANS FOR THE NEW HEMISPHERIC TRANSPORT OF AIR POLLUTANTS (HTAP) MODEL INTERCOMPARISON STUDY ROKJIN.
Evaluation and Application of Air Quality Model System in Shanghai Qian Wang 1, Qingyan Fu 1, Yufei Zou 1, Yanmin Huang 1, Huxiong Cui 1, Junming Zhao.
Modelling perspective: Key limitations of current country projection data in transboundary modelling activities. What improvements are needed? Jan Eiof.
Risks, challenges and mitigation actions in the APICE partners’ area: between the scientific findings and new governance models - Genoa M.C. Bove, P. Brotto,F.
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.
Evidence for an increase in the photochemical lifetime of ozone in the eastern United States Presented at the 14 th CMAS Meeting Wednesday October 7 th,
Chemistry-climate working group Co-chairs: Hong Liao, Shiliang Wu The 7th International GEOS-Chem Meeting (IGC7)
Chemical Condition and Surface Ozone in Urban Cities of Texas During the Last Decade: Observational Evidence from OMI, CAMS, and Model Analysis Yunsoo.
Overview of Transboundary Air Management in North America Gothenburg Protocol and Review 20 September 2006 Nav Khera and Kimber Scavo.
Georgia Institute of Technology SUPPORTING INTEX THROUGH INTEGRATED ANALYSIS OF SATELLITE AND SUB-ORBITAL MEASUREMENTS WITH GLOBAL AND REGIONAL 3-D MODELS:
‘APEC Blue’ in North China simulated with the high resolution nested GEOS-Chem model Yixuan Gu 1,2, Hong Liao 1 1 State Key Laboratory of Atmospheric Boundary.
Evaluation of emission inventory (EI) of air pollutants for Nanjing, China Y. ZHAO 1, L. Qiu 1, F. XIE 2, Q. ZHANG 3, Y. YU 4, C. NIELSEN 5, J. ZHANG 6.
Jie Zhang, Qiuyue Zhao, Guofeng Shen
Impact assessment of anthropogenic emission control upon aerosol mass burden during heavy pollution episodes over North China Plain Meigen Zhang, Xiao.
Introduction The indicator species are widely used to assess the sensitivity of ozone to the reduction of emissions of its two main precursors: nitrogen.
Student : Shen-Feng Chang Advisor : Yi-Chyun Hsu Atmospheric Environment 43 (2009) 584–593 journal homepage: Aircraft.
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.
2. Earth System Research Laboratory, Chemical Sciences Division, NOAA
The Double Dividend of Methane Control Arlene M. Fiore IIASA, Laxenburg, Austria January 28, 2003 ANIMALS 90 LANDFILLS 50 GAS 60 COAL 40 RICE 85 TERMITES.
Impacts of Meteorological Conditions Modified by Urban Expansion on Surface Ozone over Yangtz River Delta and Pearl River Delta region, China Xuemei Wang,
Ministry of Infrastructure of Ukraine (former Ministry of Transport and Communications) State Enterprise «State Road Transport Research Institute» (SE.
Using in situ data to better understand Chinese air pollution events
Xiaomeng Jin and Arlene Fiore
Yuqiang Zhang1, Owen R, Cooper2,3, J. Jason West1
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
Adverse Effects of Drought on Air Quality in the US
Urszula Parra Maza, Peter Suppan
Xiaomeng Jin1, Arlene Fiore1, Lee Murray2, Luke Valin3
FUTURE PREDICTION OF SURFACE OZONE OVER EAST ASIA UP TO 2020
Advisor: Michael McElroy
TOP-DOWN CONSTRAINTS ON EMISSION INVENTORIES OF OZONE PRECURSORS
Characteristics of Urban Ozone Formation During CAREBEIJING-2007 Experiment Zhen Liu 04/21/09.
Global Change and Air Pollution
Lily Li, Qing Lu, Jingyu An, Cheng Huang
Randall Martin Aaron Van Donkelaar Daniel Jacob Dorian Abbot
Chemical composition of ambient PM2
The Double Dividend of Methane Control
Heather Simon, Kirk Baker, Norm Possiel, Pat Dolwick, Brian Timin
Evaluating Lower Tropospheric Ozone Simulations Using GOME/SCIAMACHY/OMI Observations of NO2 and HCHO Randall Martin Aaron Van Donkelaar Chris Sioris.
Satellite Remote Sensing of Ozone-NOx-VOC Sensitivity
Space-based Diagnosis of Surface Ozone Sensitivity to Anthropogenic Emissions Randall Martin Aaron Van Donkelaar Arlene Fiore.
OMI Tropospheric NO2 in China
The relationship between summertime ozone peak hour and NOx and VOC emissions Jianfeng Li April 21, 2016.
Intercontinental Transport, Hemispheric Pollution,
Research connecting air quality, climate change, energy, policy and health J. Jason West Department of Environmental Sciences & Engineering University.
Linking Ozone Pollution and Climate Change:
INTEX-B flight tracks (April-May 2006)
Questions for consideration
Using satellite observations of tropospheric NO2 columns to infer trends in US NOx emissions: the importance of accounting for the NO2 background Rachel.
Geophysical Fluid Dynamics Laboratory Review
Geophysical Fluid Dynamics Laboratory Review
Update on 2016 AQ Modeling by EPA
2019 TEMPO Science Team Meeting
Air quality and health benefits of shale gas development in China
Update on activities of Bulgaria within/related to EMEP
Diagnostic and Operational Evaluation of 2002 and 2005 Estimated 8-hr Ozone to Support Model Attainment Demonstrations Kirk Baker Donna Kenski Lake Michigan.
How Aura transformed air quality research with a look forward to TROPOMI and geostationary satellites Daniel Jacob.
Update on specifying boundary conditions for regional-scale air quality models Mike Barna, NPS-ARD RTOWG call 9/10/19.
Fine particulate matter and ozone pollution in China: recent trends, future controls, and impact of climate change Daniel J. Jacob A typical day in Beijing.
Fig. 3 Simulated change of surface air pollution in China.
Presentation transcript:

The effect of emission control measures on ozone concentration The 9th International GEOS-Chem Meeting (IGC9) The effect of emission control measures on ozone concentration in Hangzhou during G20 meeting in 2016 Ye Wang & Hong Liao* School of Environmental Science and Engineering, Nanjing University of Information Science & Technology Good afternoon, everyone. I am Ye Wang, from NUIST. My advisor is pro. Hong Liao. And the topic of my presentation is … I am going to start with the current status of O3 pollution in China.

Current status of O3 pollution in China With the effective reduction of PM2.5 in past several years, O3 concentration increased sharply in most regions of China. Under the background of increasingly serious ozone pollution, emission reduction during G20 in 2016 provided us a typical opportunity to study if control measures could decrease ozone concentration effectively in summer. We’ll now move on to the observed air pollutants in Hangzhou during G20 under emission control. Ke Li et al., PNAS, 2018 National standard: MDA8 O3 > 160 μg m-3 (≈ 80 ppbv)

Observed air pollutants in Hangzhou during G20 under emission control Before G20 During G20 After G20 The blue dashed lines represent national standards for pollutants. It is obvious that all pollutants, except for o3, were below national standards during G20. And the mean value of MDA8 o3 during g20 was up to 160 micrograms per cubic meter. But the trend of MDA8 O3 was continuous downward. So the scientific questions are as follows: G20: 4-5 September, 2016 Period of emission control: 24 August to 6 September, 2016

Scientific questions Did emission control measures carried out during G20 reduced O3 effectively? Is it necessary to implement district-joint control measures? How sensitive is O3 concentration to emission reductions in different sectors?

Emission reductions in YRD during G20 Areas in YRD under emission control YRD CA(YRD) CA (ZJ) SCA CRA CRA: Core area SCA: Strictly controlled area CA (ZJ): Controlled area in Zhejing province CA (YRD): Controlled area in YRD Emission reductions by sectors during G20 Periods Sectors CRA SCA CA (ZJ) CA (YRD) Emission Reduction NOx (kt) VOC (ktC) VOC (ktC) 8/24-8/27 Industry 1.37 2.43 100% 1.64 2.83 50% 0.87 1.56 10.58 10.63 40% Power 0.54 0.003 1.35 0.01 30% 0.50 7.50 0.04 Residential 0.02 0.17 0.03 0.24 0.19 0.41 2.14 0%  Transport 0.98 0.66 0 % 1.46 0.91 0.90 0.58  0% 10.96 3.38 0% 8/28-9/6 3.53 5.03 4.24 5.86 2.26 3.23 27.81 22.29 1.15 2.89 1.09 16.61 0.08 0.35 0.07 0.49 0.06 0.38 1.03 4.30 2.50 1.28 3.72 1.78 2.30 1.12 27.94 6.86 According to the environmental quality guarantee scheme issued by government in 2016, areas in Yangtze River delta were divided into four parts and they are… emission reductions by sectors are described in this table. The emissions in different regions were calculated by MEIC inventory in 2016. ——Environmental Quality Guarantee Scheme, 2016.

Nested simulation over Asia Numerical experiments GEOS-Chem simulation Nested simulation over Asia Numerical experiments Version: v11-01 MET: MERRA2 Spatial resolution: 0.5°x0.625° Vertial resolution: 72 levels Resolution: 0.5°x0.625° Emission: MEIC_2016 Time: 8 August-30 September To quantify the necessity of district-joint control measures CTRLCRA CTRLZJ CTRLYRD To quantify how sensitive is O3 concentration to emission reductions in different sectors The version of GEOS-Chem model we used is 11.01, meteorological field is MERRA2 and emission inventory is MEIC in 2016. To quantify the necessity of district-joint control measures, we designed three numerical experiments and areas in CTRLZJ experiment are core area, strictly controlled area, controlled area in zj province. And ctrlYRD experiment includes all control areas. Four numerical experiments were designed to quantify how sensitive is O3 concentration to emission reductions in different sectors. And all emissions were cut down in them. CA(YRD) CTRLIND CTRLPOW CTRLRES CTRLTRA CRA SCA CA (ZJ)

Model evaluation: MDA8 O3 Observation Simulation Comparison of MDA8 O3 in Hangzhou between obs. and sim. NMB: Before G20: 21.7% During G20: 6.1% After G20: 25.0% Comparison of distribution of MDA8 O3 8 Aug. 6 Sep. Comparison of MDA8_O3 between observation and simulation in Base case were conducted to evaluate model performance. There are good agreements between simulated and observed data. Dots: observed values Contour: simulated values

Results: the effect of emission controls on O3 during G20 Comparison of MDA8_O3 in Hangzhou among OBS., BASE and CTRLYRD OBS BASE CTRLYRD CTRLYRD-BASE CTRLYRD-BASE (Percentage) Now we will move on to the results. Comparison of MDA8_O3 during G20 in Hangzhou among observation, base case and CTRLYRD experiment is shown in this picture. CTRLYRD is the actual strategy applied during G20. we can find that the values of MDA8 O3 simulated in CTRLYRD are much lower than that in base case. The mean difference of MDA8_O3 in Hangzhou between CTRLYRD experiment and base case is minus twenty one micrograms per cubic meter. Therefore, the control measures reduced O3 concentration in Hangzhou effectively. Mean difference of MDA8 O3 in Hangzhou: -21.0 μg m-3 (-11.6%) μg m-3

Results: impact of area and district-joint control on O3 during G20 BASE Reduction (Experiments-BASE) in MDA8 O3 in Hangzhou during G20: CTRLCRA (Controlling core area): -12.5 μg m-3 CTRLZJ (Controlling Zhejiang province): -16.1 μg m-3 CTRLYRD (Controlling Yangtze River Delta): -21.0 μg m-3 Difference in MDA8 O3 during G20 from control measures CTRLCRA-CTRL CTRLCRA-CTRL CTRLCRA-CTRL Let’s see the impact of area and district-joint control on O3 during G20. Comparing the reduction in MDA8 O3 in Hangzhou, it is obvious that controlling core area, Zhejiang province and Yangtze River delta could all decrease O3 concentration in Hangzhou effectively. However, controlling YRD is most effective. The distribution of absolute difference of MDA8_O3 shows the same conclusion. So it is necessary to carry out district-joint measures during G20. CA(YRD) CRA SCA CA(ZJ) μg m-3

Results: Why did O3 concentration decrease so effectively? VOCs/NOx (Base) NOx: NO+NO2 VOCs: C2H6+C3H8+ALK4+PRPE+ACET+MEK+ISOP VOCs/NOx>15: NOx-limited zone VOCs/NOx<4 : VOC-limited zone 4≤VOCs/NOx≤15: transition zone Carrillotorres et al., 2017 The ratios of VOCs to Nox in base case can explain why measures during G20 reduced ozone concentration so effectively. The reason is that … Core area and most of Zhejiang province were in transition zone; reductions in either NOx or VOCs reduce O3

Results: impact of emission reductions by sectors on O3 CTRLIND-BASE CTRLPOW-BASE Mean reductions of MDA8 O3 in Hangzhou during G20: CTRLIND: 18.85 μg m-3 CTRLPOW: 5.25 μg m-3 CTRLTRA: 12.98 μg m-3 CTRLRES: 3.14 μg m-3 CTRLTRA-BASE CTRLRES-BASE More emission reductions should be made to keep O3 below national standard during the meeting. So how sensitive is O3 concentration to emission reductions in different sectors? Mean reductions of MDA8 O3 in Hangzhou in each experiments are shown here. So controlling any sector could reduce O3 concentration when industrial emission control is most effective following by traffic emission control. It is suggested that the intensity of industrial and traffic emission control could be improved to achieve the standard.

Summary The mean difference of simulated MDA8 O3 in Hangzhou between Base and CTRLYRD during G20 is -21.0 μg m-3 (-11.6%). The control measures reduced O3 in Hangzhou effectively during G20. Comparing mean reduction of MDA8 O3 in Hangzhou during G20 in CTRLCRA, CTRLZJ and CTRLYRD, it is necessary to carry out district-joint emission control measures during G20. Comparing mean reduction of MDA8 O3 in Hangzhou during G20 in CTRLIND, CTRLPOW, CTRLRES and CTRLTRA, the intensity of industrial and traffic emission control could be improved to keep O3 below national standards. Here is my brief summary. So that’s all, thank you very much.

THANK YOU