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Characteristics of Urban Ozone Formation During CAREBEIJING-2007 Experiment Zhen Liu 04/21/09.

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Presentation on theme: "Characteristics of Urban Ozone Formation During CAREBEIJING-2007 Experiment Zhen Liu 04/21/09."— Presentation transcript:

1 Characteristics of Urban Ozone Formation During CAREBEIJING-2007 Experiment
Zhen Liu 04/21/09

2 Outline 1. Introduction and methods
2. Observed O3 precursors and their implications 3. PAN simulation with aromatics + OH methylglyoxal 4. Characteristics of ozone formation 5. Summary

3 Campaigns of Air Quality Research in Beijing and surounding Region
Adapted from Zhu’s Overview of CAREBEIJING study

4 A 1-D photochemical model
The 1-D photochemical model (e.g. Wang et al., 2008) driven by WRF assimilated meteorology fields adopts the photochemical and dry and wet deposition modules from the GEOS-CHEM model (Bey et al., 2001). The model includes a detailed photochemical mechanism with about 200 reactions and 120 concentration-varying chemical species; 24 tracers (family or species) are transported using the scheme by Walcek (2000) to describe O3-NOx–hydrocarbon chemistry. The in situ measurement data and 3D-REAM output were used to constrain the model. In situ observation and 3-D REAM output O3-NOx-hydrocarbon chemistry 200 reactions involving 120 species Transport 24 tracers, 35 vertical layers WRF Meteorology fields

5 Observed O3 precursors – NOy species
Average Daytime NOy Budget for August 2007 Total NOy: 28.2ppbv NO 17.3% NO2 29.6% HNO3 23.3% PAN 13.6% HONO 3.8% HNO4 0.06% N2O5 0.02% Residual 12.2%

6 Observed O3 precursors – VOC species
Average VOC composition Total VOC: ppbC Alkanes 31% Alkenes 5% Aromatics 64% Table 1. Comparison of the emission inventory based SSC and observed mixing ratios for aromatic species *steady state concentration SSC* from Emission Observation % Toluene 67.4 47.5 Ethyl Benzene 7.7 20.2 M,p-Xylene 4.9 19.1 7.9 O-xylene 7.2 7.5 1,3,5-trimethyl benzene 1.6 2.4 1,2,3-trimethyl benzene 2.1 1.4 1,2,4-trimethyl benzene 1.3 1.9

7 K(molec-1cm3s-1) for OH oxidation
PAN simulation with aromatics + OH methylglyoxal Table 2 Methylglyoxal yields and related reaction rate constants used in the photochemical model K(molec-1cm3s-1) for OH oxidation MGLY formation yield Toluene 6.00E-12 16.70% Ethyl Benzene 7.50E-12 / M,p-Xylene 2.10E-11 25% 1.30E-11 O-xylene 21.70% 1,3,5-trimethyl benzene 4.09E-11 90% 1,2,3-trimethyl benzene 3.13E-11 20% 1,2,4-trimethyl benzene 3.33E-11 44%

8 Ozone formation rate and HOx in different scenarios
S1: neither PAN nor HONO is constrained S2: PAN constrained with observation S3: HONO constrained with observation S4: both PAN and HONO constrained with observation S5: S2+aromaticsMGLY S6: S4+aromaticsMGLY We did six different simulations to investigate the influences of oxidant levels on ozone and radicals.

9 Ozone formation rate sensitivity to NOx levels – only standard scenario
Typical VOC limited regime What is the ozone formation regime in Beijing? VOC limited or NOx limited? Based on our simulations with 100%, 90% and 70% observed NOx, there is an anti-correlation between ozone formation rate and NOx levels. Beijing is in the VOC-limited regime. Daytime evolution

10 Summary A 1-D photochemical model was applied to analyze a full suite of atmospheric pollutants data during CAREBEIJING-2007 Experiment (August 2007). Observed oxidants (PAN and HNO2) levels are much higher than predicted from the standard model, which almost increase by 100% the ozone formation rate, as well as the HOx (OH and HO2) concentration. The abundance of aromatic VOC (~60% of total VOC in ppbC) leading to the high level of methylglyoxal appears to play a key role in PAN formation. Tests for ozone sensitivity to NOx levels indicate the typical VOC-limited mechanism of ozone formation in urban Beijing.

11 Thanks a lot!


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