日本地球惑星科学連合2014年大会

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セッション記号 U (ユニオン) » ユニオン

[U-04_29PO1] 最新の大気科学:航空機による大気科学・地球観測研究の展開

2014年4月29日(火) 14:00 〜 15:15 3階ポスター会場 (3F)

コンビーナ:*原 辰彦(建築研究所国際地震工学センター )、山田 耕(早稲田大学政治経済学術院 )、紺屋 恵子(海洋研究開発機構 地球環境変動領域 )、久利 美和(東北大学災害科学国際研究所 )、安藤 寿男(茨城大学理学部理学科地球環境科学コース )、座長:原 辰彦(建築研究所国際地震工学センター )、久利 美和(東北大学災害科学国際研究所)、山田 耕(早稲田大学政治経済学術院 )、紺屋 恵子

14:00 〜 15:15

[U04-P02] 東シナ海上空における窒素化合物の航空機観測

*定永 靖宗1坂東 博1新垣 雄光2加藤 俊吾3梶井 克純4張 代洲5渡邉 泉6藤本 敏行7奥山 喜久夫8荻 崇8瀬戸 章文9高見 昭憲10清水 厚10畠山 史郎6 (1.大阪府立大学、2.琉球大学、3.首都大学東京、4.京都大学、5.熊本県立大学、6.東京農工大学、7.室蘭工業大学、8.広島大学、9.金沢大学、10.国立環境研究所)

キーワード:航空機観測, 硝酸(塩), 反応性総窒素酸化物, 東アジア

In order to clarify long-range transport of air pollutants from the Asian continent, we have conducted aerial observation over the East China Sea and measured air pollutants centering on aerosols, as part of Grant-in-Aid for Scientific Research on Innovative Areas “Impacts of Aerosols in East Asia on Plants and Human Health (ASEPH)”. In this presentation, the results of nitrogen compounds such as nitrate are mainly described.
The aerial observations were conducted in October, 2009 (autumn), December, 2010 (winter) and March, 2012 (spring) over the East China Sea. The flights were performed between Fukue Island and the southern offing of Jeju Island and the flight altitudes were 500, 1000, 2000 and 3000 m. Onboard measurements of gaseous total odd nitrogen species, gaseous nitric acid (HNO3(g)), O3, SO2, CO and black carbon were made and particles were collected on filters for ionic and metal component analyses.
The concentration ratios of particulate nitrate (NO3-(p)) to inorganic total nitrate (T.NO3 = HNO3(g) + NO3-(p)) were less than 0.5 in most of the flights except under high concentrations of dust particles (Kosa) or transboundary air pollutants. Most of NO3-(p) would be NaNO3 formed by the reaction of gaseous nitric acid (HNO3(g)) with sea salt aerosols during the observations in autumn and winter except on October 17 and December 11, when high concentrations of Kosa were transported. In the spring observation, the fraction of NaNO3 in NO3-(p) was low and a large part of NO3-(p) would be originated from reactions of HNO3(g) with gas phase ammonia and soil dust particles.
O3 concentrations decreased with altitude in autumn and increased in winter. Positive and negative correlations between NOy-T.NO3 and O3 concentrations were observed throughout the flights in autumn and winter, respectively. This indicates that the major components of NOy-T.NO3 were secondary photochemical nitrogen oxides such as PANs and NOx, in autumn and winter, respectively. The differences of vertical distribution and NOy components between autumn and winter may be caused by the variation of solar radiation intensity.