Improvement on numerical simulation by variational assimilation of surface PM2.5 and aerosol lidar during a heavy pollution episode in winter in Tianjin
YANG Xu1,2, FAN Wen-yan1,2, CAI Zi-ying1,2, ZHU Yu-qiang1,2, TANG Ying-xiao1,2, DONG Qi-ru3
1. Tianjin Environmental Meteorological Center, Tianjin 300074, China; 2. CMA-NKU Cooperative Laboratory for Atmospheric Environment-Health Research, Tianjin 300074, China; 3. Tianjin Institute of Meteorological Science, Tianjin 300074, China
Abstract:For the transport-type heavy pollution episodes, the vertical simulation deviation of atmospheric chemical model was large, the ground observation assimilation could not significantly improve the vertical initial field of pollution, and the upper air transport was underestimated. A heavy pollution episode was taken as an example in Tianjin, which occurred from January 5 to 6, 2023, the aerosol variational assimilation technology was developed for the joint application of surface PM2.5 and aerosol lidar vertical observations, to improve the vertical pollution simulation of atmospheric chemical model and serve forecast, early warning and mechanism analysis of heavy pollution episodes. The results showed that during the heavy pollution episode, growth rate and peak concentration of ground PM2.5 was significantly underestimated, simulated pollution layer height was about 200~300m lower than observed value and characteristics such as higher PM2.5 concentration in upper air than that on the ground in transportation phase of daytime and high pollution values above the stable boundary layer at night were not effectively reflected; Assimilation of surface PM2.5 observations effectively optimized PM2.5 spatial distribution, average simulation error decreased by 35.3μg/m3 and 77.3μg/m3 respectively in Shijiazhuang and Hengshui, the upstream cities and decreased by 39.7μg/m3 in Tianjin. However, its improvement on vertical distribution simulation was limited, especially for the complex change of PM2.5 vertical distribution in transport-type pollution episode, which was not accurately reflected. By adding assimilation of vertical PM2.5 observations obtained from aerosol lidar, vertical PM2.5 simulation was further improved, the maximum reduction of PM2.5 mass concentration RMSE was 19.8μg/m3 at about 500m. There was obvious positive effect at the assimilated time and within 2~3h, as for subsequent time, simulated pollution layer height was basically same with observation in S2 phase, the difference between them reduced to 50~100m, compared with 200~300m in CTRL experiment without assimilation and 100~200m in DA_SFC experiment with surface PM2.5 assimilation. High value of pollution above stable boundary layer was effectively simulated and the simulation error of PM2.5 mass concentration in the heavy polluted layer was significantly reduced; Assimilation effect in the daytime on January 5 was not good as that of S2 phase, accurate simulation of vertical PM2.5 could be achieved in a short time, but the deviation of vertical simulation had been significantly enlarged again with simulation time increasing. In spite of this, positive effect still existed compared with DA_SFC and the simulation error of pollution layer height was reduced by at least 50m.
杨旭, 樊文雁, 蔡子颖, 朱玉强, 唐颖潇, 董琪如. 地面PM2.5和气溶胶激光雷达联合变分同化对天津冬季一次重污染过程数值模拟改进研究[J]. 中国环境科学, 2023, 43(10): 5088-5097.
YANG Xu, FAN Wen-yan, CAI Zi-ying, ZHU Yu-qiang, TANG Ying-xiao, DONG Qi-ru. Improvement on numerical simulation by variational assimilation of surface PM2.5 and aerosol lidar during a heavy pollution episode in winter in Tianjin. CHINA ENVIRONMENTAL SCIENCECE, 2023, 43(10): 5088-5097.
韩素芹,冯银厂,边海,等.天津大气污染物日变化特征的WRF-Chem数值模拟[J]. 中国环境科学, 2008,28(9):828-832. Han S Q, Feng Y C, Bian H, et al. Numerical simulation of diurnal variation of major pollutants with WRF-Chem model in Tianjin[J]. China Environmental Science, 2008,28(9):828-832.
[2]
李珊珊,程念亮,徐峻,等.2014年京津冀地区PM2.5浓度时空分布及来源模拟[J]. 中国环境科学, 2015,35(10):2908-2916. Li S S, Cheng N L, Xu J, et al. Spatial and temporal distributions and source simulation of PM2.5 in Beijing-Tianjin-Hebei region in 2014[J]. China Environmental Science, 2015,35(10):2908-2916.
[3]
Zhang L, Gong S, Zhao T, et al. Development of WRF/CUACE v1.0model and its preliminary application in simulating air quality in China[J]. Geoscientific Model Development, 2021,14(2):703-718.
[4]
崔应杰,王自发,朱江,等.空气质量数值模式预报中资料同化的初步研究[J]. 气候与环境研究, 2006,11(5):616-626. Cui Y J, Wang Z F, Zhu J, et al. A preliminary study on data assimilation for numerical air quality model prediction[J]. Climatic and Environmental Research (in Chinese), 2006,11(5):616-626.
[5]
Tombette M, Mallet V, Sportisse B. PM10 data assimilation over Europe with the optimal interpolation method[J]. Atmospheric Chemistry and Physics, 2009,9(1):57-70.
[6]
Lin C, Wang Z, Zhu J. An Ensemble Kalman Filter for severe dust storm data assimilation over China[J]. Atmospheric Chemistry and Physics, 2008,8(11):2975-2983.
[7]
Pagowski M, Grell G A. Experiments with the assimilation of fine aerosols using an ensemble Kalman filter[J]. J. Geophys. Res., 2012,117:D21302.
[8]
Peng Z, Liu Z Q, Chen D, et al. Improving PM2.5forecast over China by the joint adjustment of initial conditions and source emissions with an ensemble Kalman filter[J]. Atmospheric Chemistry and Physics, 2017, 17:4837-4855.
[9]
Jiang Z Q, Liu Z Q, Wang T J, et al. Probing into the impact of 3DVAR assimilation of surface PM10 observations over China using process analysis[J]. Journal of Geophysical Research:Atmospheres, 2013,118(12):6738-6749.
[10]
Feng S Z, Jiang F, Jiang Z Q, et al. Impact of 3DVAR assimilation of surface PM2.5 observations on PM2.5 forecasts over China during wintertime[J]. Atmospheric Environment, 2018,187:34-49.
[11]
靳璐滨,臧增亮,潘晓滨,等.PM2.5和PM2.5~10资料同化及在南京青奥会期间的应用试验[J]. 中国环境科学, 2016,36(2):331-341. Jin L B, Zang Z L, Pan X B, et al. Data assimilation and application experiments of PM2.5 and PM2.5~10 during Nanjing Youth Olympic Games[J]. China Environmental Science, 2016,36(2):331-341.
[12]
陈杰,李正强,常文渊,等.基于改进GSI系统的气溶胶变分同化对WRF-Chem PM2.5分析和预报的影响评估[J]. 大气与环境光学学报, 2020,15(5):321-333. Chen J, Li Z Q, Chang W Y, et al. Impact evaluation of aerosol variational assimilation based on improved GSI system on WRF-Chem PM2.5 analysis and forecast[J]. J. Atmospheric and Environmental Optics, 2020,15(5):321-333.
[13]
蔡子颖,唐邈,肖致美,等.基于源反演和气溶胶同化方法天津空气质量模式预报能力改进[J]. 环境科学, 2022,43(5):2415-2426. Cai Z Y, Tang M, Xiao Z M, et al. Improvement of environmental model prediction based on inversion and aerosol assimilation[J]. Environmental Science, 2022,43(5):2415-2426.
[14]
Zang Z L, Li Z J, Pan X B, et al. Aerosol data assimilation and forecasting experiments using aircraft and surface observations during CalNex[J]. Tellus B:Chemical and Physical Meteorology, 2016,68(1):29812.
[15]
张艳品,陈静,钤伟妙,等.石家庄冬季典型污染过程气溶胶激光雷达观测[J]. 中国环境科学, 2020,40(10):4205-4215. Zhang Y P, Chen J, Qian W M, et al. Aerosol lidar observation of typical pollution process in Shijiazhuang in Winter[J]. China Environmental Science, 2020,40(10):4205-4215.
[16]
Yumimoto K, Uno I, Sugimoto N, et al. Adjoint inversion modeling of Asian dust emission using lidar observations[J]. Atmospheric Chemistry And Physics, 2008,8(11):2869-2884.
[17]
Wang Y, Sartelet K N, Bocquet M, et al. Assimilation of ground versus lidar observations for PM10 forecasting[J]. Atmospheric Chemistry and Physics, 2013,13:269-283.
[18]
Wang Y, Sartelet K N, Bocquet M, et al. Assimilation of lidar signals:Application to aerosol forecasting in the western Mediterranean basin[J]. Atmospheric Chemistry and Physics, 2014b,14:12031-12053.
[19]
郑海涛.地面及激光雷达观测数据同化对PM2.5预报的改进[D]. 合肥:中国科学技术大学, 2018. Zheng H T. Improvement of PM2.5 Forecast by data assimilation of ground and Lidar observation[D]. Hefei:University of Science and Technology of China, 2018.
[20]
Xiang Y, Zhang T S, Ma C Q, et al. Lidar vertical observation network and data assimilation reveal key processes driving the 3-D dynamic evolution of PM2.5 concentrations over the North China Plain[J]. Atmospheric Chemistry and Physics, 21,7023-7037,2021.
[21]
Cheng X H, Liu Y L, Xu X D, et al. Lidar data assimilation method based on CRTM and WRF-Chem models and its application in PM2.5 forecasts in Beijing[J]. Science of the Total Environment, 2019, 682:541-552.
[22]
Liang Y F, Zang Z L, Liu D, et al. Development of a three-dimensional variational assimilation system for lidar profile data based on a size-resolved aerosol model in WRF-Chem model v3.9.1and its application in PM2.5 forecasts across China[J]. Geoscientific Model Development, 13,6285-6301,2020.
[23]
蔡子颖,杨旭,韩素芹,等.基于天气背景天津大气污染输送特征分析[J]. 环境科学, 2020,41(11):4855-4863. Cai Z Y, Yang X, Han S Q, et al. Transport characteristics of air pollution in Tianjin based on weather background[J]. Environmental Science, 2020,41(11):4855-4863.
[24]
王晓琦,郎建垒,程水源,等.京津冀及周边地区PM2.5传输规律研究[J]. 中国环境科学, 2016,36(11):3211-3217. Wang X Q, Lang J L, Cheng S Y, et al. Study on transportation of PM2.5 in Beijng-Tianjin-Hebei (BTH) and its surrounding area[J]. China Environmental Science, 2016,36(11):3211-3217.
[25]
杨旭,蔡子颖,韩素芹,等.基于无人机探空和数值模拟天津一次重污染过程分析[J]. 环境科学, 2021,42(1):9-18. Yang X, Cai Z Y, Han S Q, et al. Heavy pollution episode in Tianjin based on UAV meteorological sounding and numerical model[J]. Environmental Science, 2021,42(1):9-18.
[26]
Li M., Liu H, Geng G, et al. Anthropogenic emission inventories in China:a review[J]. National Science Review, 2017,4:834-866.
[27]
Li Z, Zang Z, Li Q, et al. A three-dimensional variational data assimilation system for multiple aerosol species with WRF/Chem and an application to PM2.5 prediction[J]. Atmospheric Chemistry and Physics, 2013,13(8):4265-4278.
[28]
杨旭,唐颖潇,蔡子颖,等.基于气溶胶三维变分同化天津PM2.5数值预报研究[J]. 中国环境科学, 2021,41(12):5476-5484. Yang X, Tang Y X, Cai Z Y, et al. Impact of aerosol data assimilation with 3-DVAR method on PM2.5 forecast over Tianjin[J]. China Environmental Science, 2021,41(12):5476-5484.
[29]
Lv L H, Liu W Q, Zhang T S, et al. Observations of particle extinction, PM2.5 mass concentration profile and flux in north China based on mobile lidar technique[J]. Atmospheric Environment, 2017,164:360- 369.
[30]
Tao Z M, Wang Z Z, Yang S J, et al. Profiling the PM2.5 mass concentration vertical distribution in the boundary layer[J]. Atmospheric Measurement Techniques, 2016,9:1369-1376.