Integration of multi-phase chemistries into a 3D photochemical transport model to improve model performances
- Abstract
- In recent years, many studies have emphasized that the dangers of air pollutants such as O3 and particulate matter (PM) influencing premature mortality and adverse health effects. In response to these issues, governments have implemented emission control strategies based on the result of air quality models. However, such mitigating air pollutant policies proves to be highly ineffective due to uncertainties in model simulation. These findings suggest a critical need for further development focused on enhancing model performance and reliability. In this context, we developed updated Community Multiscale Air Quality (CMAQ) model that incorporates multiphase reactions and updated emissions associated with four representative processes: (i) HONO processes, (ii) halogen processes, (iii) sulfate processes, and (iv) HO₂ processes. In particular, these four processes were selected because of their close association with the formation of air pollutants. Based on the modeling framework, we evaluate the model performance against observations, then examined the impact of the four processes on atmospheric species. First, we incorporated newly HONO processes into our modeling system to simulate accurate key atmospheric species such as O3 and PM2.5. The HONO chemistry incorporated in this study were: (i) direct HONO emissions (such as soil, traffic and soil HONO emissions); (ii) gas-phase HONO reaction; (iii) heterogeneous reactions of NO2 on aerosol and ground surfaces; (iv) renoxifications. After establishing modeling framework, we explored the impact of HONO processes on oxidant capacity (OH, HO2, and O3), as well as particulate matter concentrations. As a result, the updated model showed improvements in the mixing ratios of both HONO and O3 simulated compared to observed mixing ratios with enhanced statistical metrics. Secondly, we investigated the influence of halogen radicals (Cl, Br, and I) on significant atmospheric species by incorporating halogen processes, including emissions of halogen compounds and 155 new gaseous-, 4 aqueous-, and 18 heterogeneous-halogen reactions, into the CMAQ model. We evaluate the updated model performance by utilizing the ClNO2 observations, and then examined the net Ox production rates (P(Ox)) in the presence of the halogen radicals. The results revealed that mixing ratios of ClNO2 simulated agreed well with observations, with the index of agreement (IOA) rising from 0.41 to 0.66. In addition, the P(Ox) increased in the land, while decreased over the ocean. Our findings highlight the critical role of halogen chemistry determining the levels of atmospheric species. Thirdly, in order to address underestimation in sulfate concentrations simulated, we developed a new parameterization of the SO2 uptake coefficient (γSO2) as a function of relative humidity, and NO2 and NH3 mixing ratios. We then evaluated the γSO2 used in this study, together with different parameterizations of γSO2 introduced in previous studies. Comparative analysis showed that our study has the best agreements with surface-observations. For example, sulfate concentrations simulated in our study increasing from 3.85 μg/m3 to 4.78 μg/m3, with the IOA increasing from 0.63 to 0.70. In addition, for extended 1-year simulations, our approach also significantly reproduced the sulfate concentrations during the spring and winter. It implied that the importance of accurate γSO2 for effective air quality management strategies. Finally, we attempted to provide a comprehensive insight into the HO2 processes in the atmosphere. From the findings in aircraft observations, we found that the mixing ratios of HO2 simulated may be strongly connected with NO distributions. In particular, for low-NO conditions (below 0.3 ppb), the mixing ratios of HO2 simulated overestimated by 6.0% due to missing removal pathways. In this context, we incorporated HO2 aerosol uptake, adopting an uptake coefficient of HO2 as 0.08, assuming no H2O2 production, which can lead to improved model performance. We also explored the impact of HO2 aerosol uptake on air pollutants depending on NO mixing ratios. As a result, this study emphasized complex interactions of HO₂ in atmospheric chemistry. In this study, we attempted to achieve three major objectives: (i) incorporate missing pathways into the CMAQ model using ‘state-of-the-art’ techniques; (ii) enhance the simulation accuracy for various substances; (iii) understand their interactions in the atmosphere. To establish the purpose, we investigated four representative atmospheric processes in terms of various perspectives. Based on the result, our findings are expected to provide a valuable opportunity to expand our knowledge on atmospheric chemistry and model development.
- Author(s)
- 김기연
- Issued Date
- 2025
- Type
- Thesis
- URI
- https://scholar.gist.ac.kr/handle/local/19410
- Department
- 대학원 환경에너지공학부
- Advisor
- Song, Chul Han
- Table Of Contents
- ABSTRACT i
CONTENTS iv
LIST OF FIGURE ix
LIST OF TABLES xvi
I. Introduction 1
1.1 Research Background 1
1.2 Organization of this study 4
1.3 References 5
II. Description of methodology 7
2.1 Modeling Framework 7
2.1.1 WRF simulation 7
2.1.2 CMAQ simulation 8
2.1.3 Emission 10
2.2 KORUS-AQ campaign 11
2.3 In-situ observations 12
2.4 Korean Flexible Chemistry (KFC) Editor 14
2.5 Statistical metrics 19
2.6 References 20
III. An investigation into atmospheric nitrous (HONO) processes in South Korea 22
3.1 Introduction 22
3.2 Methodology 25
3.2.1 WRF-CMAQ model configuration 25
3.2.2 Measurements 27
3.2.3 HONO sources 32
3.2.3.1 Gas Phase reactions (GAS) 32
3.2.3.2 Biomass burning emissions (BioB) 33
3.2.3.3 Traffic emissions (TRAF) 34
3.2.3.4 Soil emission (SOIL) 35
3.2.3.5 Heterogeneous reaction of NO2 on atmospheric aerosol surfaces (HET_A) 35
3.2.3.6 Heterogeneous reaction of NO2 on tree leaf and building surfaces (HET_L and HET_BD)
- 37
3.2.3.7 Photolysis reactions (RENOx) 37
3.3 Results and Discussions 39
3.3.1 Observed vs Simulated HONO mixing ratios 39
3.3.2 Relative contribution of HONO sources 44
3.3.3 Impact of HONO processes on atmospheric species 48
3.3.3.1 Impact on atmospheric species 48
3.3.3.2 Impact on net ozone production 52
3.4 Conclusions 54
3.5 References 56
IV. Incorporation of a multiphase halogen chemistry into the Community Multiscale Air Quality (CMAQ)
model 64
4.1 Introduction 64
4.2 Methodology 66
4.2.1 Observation data 66
4.2.2 WRF-CMAQ model description 66
4.2.3 Halogen emissions 68
4.2.3.1 Anthropogenic emissions 68
4.2.3.2 Natural emissions 71
4.2.4 Halogen chemical reactions 73
4.2.4.1 Chlorine reactions 73
4.2.4.2 Bromine reactions 78
4.2.4.3 Iodine reactions 81
4.2.5 Experimental design 84
4.3 Results and Discussions 85
4.3.1 Model performances 85
4.3.1.1 Observed vs Modeled ClNO2 mixing ratios 85
4.3.1.2 Contributions to mixing ratios of ClNO2 88
4.3.1.3 Uncertainties in Cl2 91
4.3.2 Influence of the halogen chemistry on O3 mixing ratios 92
4.3.2.1 Comparative analysis at three supersites 92
4.3.2.2 Impacts of halogen processes 94
4.3.2.3 Net Ox production 97
4.3.3 Impacts of halogen chemistry on atmospheric species 100
4.4 Summary and Conclusions 104
4.5 References 106
V. A new approach for parameterization of uptake coefficient of SO2 and its impact on sulfate
concentration 110
5.1 Introduction 110
5.2 Materials and Methods 112
5.2.1 Description of WRF-CMAQ simulation 112
5.2.2 In-situ measurements 113
5.2.3 Embedded sulfate formation pathways in the CMAQ model 114
5.2.4 Heterogeneous reaction of SO2 on aerosol 116
5.3 Results and Discussions 118
5.3.1 Evaluation of biases for sulfur species in the CMAQ model 118
5.3.2 Implementation of new parameterization of γSO2 119
5.3.3 Insights into seasonal variations of sulfate concentrations 123
5.3.4 Uncertainties in sulfate formation 125
5.4 Summary 130
5.5 References 131
VI. Comprehensive insights into HO2 processes and the impact of HO2 aerosol uptake on air quality
136
6.1 Introduction 136
6.2 Methodology 138
6.2.1 Overview of WRF-CMAQ model framework 138
6.2.2 KORUS-AQ campaign 140
6.2.3 Description of HO2 aerosol loss 140
6.3 Results and Discussions 142
viii
6.3.1 Investigation of determining factor for HO2 levels 142
6.3.2 Dependence of HO2 distribution on NO mixing ratios 147
6.3.2.1 Low-NO condition 147
6.3.2.2 High-NO condition 149
6.3.3 Influence of HO2 aerosol loss on atmospheric species 151
6.3.3.1 OH, HO2, and H2O2 151
6.3.3.2 O3 152
6.3.3.3 PM2.5 156
6.4 Summary 159
6.5 References 160
VII. Summary and future study 166
7.1 Summary 166
7.2 Future study 168
7.2.1 Integration of organic aerosol chemistry 168
7.2.2 Application for different periods 168
7.2.3 Reconciliation of emission inventory 168
CURRICULUM VITA 169
ACKNOWLEDGEMENT 173
- Degree
- Doctor
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