Enhancement of the polynomial functions response surface model for real-time analyzing ozone sensitivity

Jiangbo Jin , Yun Zhu , Jicheng Jang , Shuxiao Wang , Jia Xing , Pen-Chi Chiang , Shaojia Fan , Shicheng Long

Front. Environ. Sci. Eng. ›› 2021, Vol. 15 ›› Issue (2) : 31

PDF (5921KB)
Front. Environ. Sci. Eng. ›› 2021, Vol. 15 ›› Issue (2) : 31 DOI: 10.1007/s11783-020-1323-0
RESEARCH ARTICLE
RESEARCH ARTICLE

Enhancement of the polynomial functions response surface model for real-time analyzing ozone sensitivity

Author information +
History +
PDF (5921KB)

Abstract

• The calculation process and algorithm of response surface model (RSM) were enhanced.

• The prediction errors of RSM in the margin and transition areas were greatly reduced.

• The enhanced RSM was able to analyze O3-NOx-VOC sensitivity in real-time.

• The O3 formations were mainly sensitive to VOC, for the two case study regions.

Quantification of the nonlinearities between ambient ozone (O3) and the emissions of nitrogen oxides (NOx) and volatile organic compound (VOC) is a prerequisite for an effective O3 control strategy. An Enhanced polynomial functions Response Surface Model (Epf-RSM) with the capability to analyze O3-NOx-VOC sensitivities in real time was developed by integrating the hill-climbing adaptive method into the optimized Extended Response Surface Model (ERSM) system. The Epf-RSM could single out the best suited polynomial function for each grid cell to quantify the responses of O3 concentrations to precursor emission changes. Several comparisons between Epf-RSM and pf-ERSM (polynomial functions based ERSM) were performed using out-of-sample validation, together with comparisons of the spatial distribution and the Empirical Kinetic Modeling Approach diagrams. The comparison results showed that Epf-RSM effectively addressed the drawbacks of pf-ERSM with respect to over-fitting in the margin areas and high biases in the transition areas. The O3 concentrations predicted by Epf-RSM agreed well with Community Multi-scale Air Quality simulation results. The case study results in the Pearl River Delta and the north-western area of the Shandong province indicated that the O3 formations in the central areas of both the regions were more sensitive to anthropogenic VOC in January, April, and October, while more NOx-sensitive in July.

Graphical abstract

Keywords

Response surface model / Hill-climbing algorithm / Ozone pollution / Precursor emissions / Control strategy

Cite this article

Download citation ▾
Jiangbo Jin, Yun Zhu, Jicheng Jang, Shuxiao Wang, Jia Xing, Pen-Chi Chiang, Shaojia Fan, Shicheng Long. Enhancement of the polynomial functions response surface model for real-time analyzing ozone sensitivity. Front. Environ. Sci. Eng., 2021, 15(2): 31 DOI:10.1007/s11783-020-1323-0

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Cardelino C A, Chameides W L (1995). An observation-based model for analyzing ozone precursor relationships in the urban atmosphere. Journal of the Air & Waste Management Association, 45(3): 161–180

[2]

Cardelino C A, Chameides W L (2000). The application of data from photochemical assessment monitoring stations to the observation-based model. Atmospheric Environment, 34(12–14): 2325–2332

[3]

Chen X, Situ S P, Zhang Q, Wang X M, Sha C Y, Zhouc L Y, Wu L Q, Wu L L, Ye L M, Li C (2019). The synergetic control of NO2 and O3 concentrations in a manufacturing city of southern China. Atmospheric Environment, 201: 402–416

[4]

Collet S, Kidokoro T, Karamchandani P, Shah T (2018). Future-year ozone isopleths for South Coast, San Joaquin Valley, and Maryland. Atmosphere, 9(9): 354

[5]

Ding D, Xing J, Wang S X, Chang X, Hao J M (2019). Impacts of emissions and meteorological changes on China’s ozone pollution in the warm seasons of 2013 and 2017. Frontiers of Environmental Science & Engineering, 13(5): 76

[6]

Fang T, Zhu Y, Jang J, Wang S, Xing J, Chiang P C, Fan S, You Z, Li J (2020). Real-time source contribution analysis of ambient ozone using an enhanced meta-modeling approach over the Pearl River Delta Region of China. Journal of Environmental Management, 268: 110650

[7]

Guindon S, Gascuel O (2003). A simple, fast, and accurate algorithm to estimate large phylogenies by maximum likelihood. Systematic Biology, 52(5): 696–704

[8]

Hammersley J M (1960). Monte Carlo methods for solving multivariable problems. Annals of the New York Academy of Sciences, 86(3): 844–874

[9]

Heyes C, Schöpp W, Amann M, Bertok I, Cofala J, Gyarfas F, Klimont Z, Makowski M, Shibayev S (1997). A model for optimizing strategies for controlling ground-level ozone in Europe. Laxenburg: International Institute for Applied Systems Analysis

[10]

Heyes C, Schöpp W, Amann M, Unger S (1996). A reduced-form model to predict long-term ozone concentrations in Europe. Laxenburg: International Institute for Applied Systems Analysis

[11]

Liao K J, Tagaris E, Manomaiphiboon K, Napelenok S L, Woo J H, He S, Amar P, Russell A G (2007). Sensitivities of ozone and fine particulate matter formation to emissions under the impact of potential future climate change. Environmental Science & Technology, 41(24): 8355–8361

[12]

Lin H W, Sun L J (2015). Searching globally optimal parameter sequence for defeating Runge phenomenon by immunity genetic algorithm. Applied Mathematics and Computation, 264: 85–98

[13]

Lozano M, Herrera F, Krasnogor N, Molina D (2004). Real-coded memetic algorithms with crossover hill-climbing. Evolutionary Computation, 12(3): 273–302

[14]

Ma Q A, Cai S Y, Wang S X, Zhao B, Martin R V, Brauer M, Cohen A, Jiang J K, Zhou W, Hao J M, Frostad J, Forouzanfar M H, Burnett R T (2017). Impacts of coal burning on ambient PM2.5 pollution in China. Atmospheric Chemistry and Physics, 17(7): 4477–4491

[15]

Ou J M, Yuan Z B, Zheng J Y, Huang Z J, Shao M, Li Z K, Huang X B, Guo H, Louie P K K (2016). Ambient ozone control in a photochemically active region: Short-term despiking or long-term attainment? Environmental Science & Technology, 50(11): 5720–5728

[16]

Pu X, Wang T J, Huang X, Melas D, Zanis P, Papanastasiou D K, Poupkou A (2017). Enhanced surface ozone during the heat wave of 2013 in Yangtze River Delta region, China. Science of the Total Environment, 603: 807–816

[17]

Seltzer K M, Shindell D T, Malley C S (2018). Measurement-based assessment of health burdens from long-term ozone exposure in the United States, Europe, and China. Environmental Research Letters, 13(10): 104018

[18]

Sharma S, Chatani S, Mahtta R, Goel A, Kumar A (2016). Sensitivity analysis of ground level ozone in India using WRF-CMAQ models. Atmospheric Environment, 131: 29–40

[19]

Su R, Lu K D, Yu J Y, Tan Z F, Jiang M Q, Li J, Xie S D, Wu Y S, Zeng L M, Zhai C Z, Zhang Y H (2018). Exploration of the formation mechanism and source attribution of ambient ozone in Chongqing with an observation-based model. Science China. Earth Sciences, 61(1): 23–32

[20]

Sun L, Xue L K, Wang Y H, Li L L, Lin J T, Ni R J, Yan Y Y, Chen L L, Li J, Zhang Q Z, Wang W X (2019). Impacts of meteorology and emissions on summertime surface ozone increases over central eastern China between 2003 and 2015. Atmospheric Chemistry and Physics, 19(3): 1455–1469

[21]

Tan Z F, Lu K D, Dong H B, Hu M, Li X, Liu Y H, Lu S H, Shao M, Su R, Wang H C, Wu Y S, Wahner A, Zhang Y H (2018a). Explicit diagnosis of the local ozone production rate and the ozone-NOx-VOC sensitivities. Science Bulletin, 63(16): 1067–1076

[22]

Tan Z F, Lu K D, Jiang M Q, Su R, Dong H B, Zeng L M, Xie S D, Tan Q W, Zhang Y H (2018b). Exploring ozone pollution in Chengdu, southwestern China: A case study from radical chemistry to O3-VOC-NOx sensitivity. Science of the Total Environment, 636: 775–786

[23]

Wang N, Lyu X P, Deng X J, Huang X, Jiang F, Ding A J (2019). Aggravating O3 pollution due to NOx emission control in eastern China. Science of the Total Environment, 677: 732–744

[24]

Wang T, Xue L K, Brimblecombe P, Lam Y F, Li L, Zhang L (2017). Ozone pollution in China: A review of concentrations, meteorological influences, chemical precursors, and effects. Science of the Total Environment, 575: 1582–1596

[25]

Xing J, Ding D, Wang S X, Dong Z X, Kelly J T, Jang C, Zhu Y, Hao J M (2019). Development and application of observable response indicators for design of an effective ozone and fine-particle pollution control strategy in China. Atmospheric Chemistry and Physics, 19(21): 13627–13646

[26]

Xing J, Ding D, Wang S X, Zhao B, Jang C, Wu W J, Zhang F F, Zhu Y, Hao J M (2018). Quantification of the enhanced effectiveness of NOx control from simultaneous reductions of VOC and NH3 for reducing air pollution in the Beijing-Tianjin-Hebei region, China. Atmospheric Chemistry and Physics, 18(11): 7799–7814

[27]

Xing J, Wang S X, Jang C, Zhu Y, Hao J M (2011). Nonlinear response of ozone to precursor emission changes in China: A modeling study using response surface methodology. Atmospheric Chemistry and Physics, 11(10): 5027–5044

[28]

Xing J, Wang S X, Zhao B, Wu W J, Ding D A, Jang C, Zhu Y, Chang X, Wang J D, Zhang F F, Hao J M (2017). Quantifying nonlinear multiregional contributions to ozone and fine particles using an updated response surface modeling technique. Environmental Science & Technology, 51(20): 11788–11798

[29]

Xue L K, Wang T, Gao J, Ding A J, Zhou X H, Blake D R, Wang X F, Saunders S M, Fan S J, Zuo H C, Zhang Q Z, Wang W X (2014). Ground-level ozone in four Chinese cities: precursors, regional transport and heterogeneous processes. Atmospheric Chemistry and Physics, 14(23): 13175–13188

[30]

Yang W, Chen H, Wang W, Wu J, Li J, Wang Z, Zheng J, Chen D (2019). Modeling study of ozone source apportionment over the Pearl River Delta in 2015. Environmental pollution (Barking, Essex: 1987), 253: 393–402

[31]

Yao Y R, He C, Li S Y, Ma W C, Li S, Yu Q, Mi N, Yu J, Wang W, Yin L, Zhang Y (2019). Properties of particulate matter and gaseous pollutants in Shandong, China: Daily fluctuation, influencing factors, and spatiotemporal distribution. Science of the Total Environment, 660: 384–394

[32]

Ye L M, Wang X M, Fan S F, Chen W H, Chang M, Zhou S Z, Wu Z Y, Fan Q (2016). Photochemical indicators of ozone sensitivity: Application in the Pearl River Delta, China. Frontiers of Environmental Science & Engineering, 10(6): 15

[33]

Yue X, Unger N, Harper K, Xia X, Liao H, Zhu T, Xiao J, Feng Z, Li J (2017). Ozone and haze pollution weakens net primary productivity in China. Atmospheric Chemistry and Physics, 17(9): 6073–6089

[34]

Zhang K, Xu J L, Huang Q, Zhou L, Fu Q Y, Duan Y S, Xiu G L (2020). Precursors and potential sources of ground-level ozone in suburban Shanghai. Frontiers of Environmental Science & Engineering, 14(6): 92

[35]

Zhong J, Cai X M, Bloss W J (2014). Modelling segregation effects of heterogeneous emissions on ozone levels in idealised urban street canyons: Using photochemical box models. Environmental Pollution, 188: 132–143

RIGHTS & PERMISSIONS

Higher Education Press

AI Summary AI Mindmap
PDF (5921KB)

Supplementary files

FSE-20105-OF-JJB_suppl_1

2268

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/