日本地球惑星科学連合2024年大会

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セッション記号 H (地球人間圏科学) » H-CG 地球人間圏科学複合領域・一般

[H-CG26] 農業残渣焼却のもたらす大気汚染と健康影響および解決への道筋

2024年5月26日(日) 15:30 〜 16:45 102 (幕張メッセ国際会議場)

コンビーナ:林田 佐智子(総合地球環境学研究所/奈良女子大学)、Patra Prabir(Research Institute for Global Change, JAMSTEC)、山地 一代(神戸大学)、座長:山地 一代(神戸大学)、安富 奈津子(総合地球環境学研究所)

15:45 〜 16:00

[HCG26-07] Numerical analysis of PM pollution after Kharif-crop harvest over the Delhi-Haryana-Punjab region by combining regional model simulations and field observations

*山地 一代1,2、辻 彩弥加1梶野 瑞王3,2林田 佐智子2、Singh Tanbir4、安富 奈津子2、荒木 晶2Biswal Akash2Mangaraj Poonam2松見 豊5,2中山 智喜6,2滝川 雅之7Patra Prabir2,7 (1.神戸大学、2.総合地球環境学研究所、3.気象研究所、4.SCVB Government College、5.名古屋大学、6.長崎大学、7.海洋研究開発機構)

キーワード:PM2.5汚染、領域大気質モデル、乾季インド北西部、農業残渣焼却

The remarkable increase in air pollution over the megacities of South Asia has attracted worldwide attention. Compared to the recommendation for PM2.5, e.g. 25 μgm-3 24-hour average, in the World Health Organization's Air Quality Guidelines (AQGs) or that of the Indian government (~60 μgm-3), the PM2.5 concentration level in the National Capital Region (NCR) of Delhi, India is significantly higher. Especially during the dry season after the kharif crop harvest, from October to February, pollution levels tend to be worse over the Delhi NCR and its environs, which is believed to be affected by seasonally increased anthropogenic emissions, such as post-harvest burning of straw stubble over the extensive grain-growing region of northwestern India, in addition to the stagnation of atmospheric pollutants due to meteorological conditions.
The AAKASH project has conducted intensive field campaigns using Compact and Useful PM2.5 Instrument with Gas Sensors (CUPI-Gs) in the states of Punjab, Haryana and Delhi NCR from September to November 2022 and 2023. These campaigns were found to increase PM2.5 concentrations above 400 µgm3 in Delhi NCR, and during this time, the polluted air masses influenced by the Crop Residue Burning (CRB) were expected to be transported from Punjab to Haryana and Delhi.
A regional air quality modeling system using WRF/CMAQ incorporating emission inventories, HTAPv2.1, and GFASv2.1 seemed reasonable enough to simulate PM2.5 concentrations in the Delhi-Haryana-Punjab region except during the early dry season, October to November. For the early dry season, the modeling system tends to underestimate observed PM2.5 concentrations. The modeled sensitivity experiments for CRB emissions somehow explained the PM2.5 underestimations by the model in Punjab. One of the remaining issues in the PM2.5 simulation would be uncertainties in the emissions, especially related to small-scale post-harvest straw stubble burning and other unknown emission sources. The other problems would also be inherent in some mechanisms of the model during air mass transport. After presenting the current status of the air quality model, the spatial and temporal variations of post-harvest air pollutants over the Delhi-Haryana-Punjab region will be discussed.

[Acknowledgements]
This research is financially supported by Research Institute for Humanity and Nature (RIHN: a constituent member of NIHU) Project No. 14200133 (Aakash). The intensive field campaigns were conducted with supports from all participants of the network observations in Aakash project.