*Yasuhiro SADANAGA1, Hiroshi BANDOW1, Takemitsu ARAKAKI2, Shungo KATO3, Yoshizumi KAJII4, Daizhou ZHANG5, Izumi WATANABE6, Toshiyuki FUJIMOTO7, Kikuo OKUYAMA8, Takashi OGI8, Takafumi SETO9, Akinori TAKAMI10, Atsushi SHIMIZU10, Shiro HATAKEYAMA6
(1.Osaka Prefecture University, 2.University of the Ryukyus, 3.Tokyo Metropolitan University, 4.Kyoto University, 5.Prefectural University of Kumamoto, 6.Tokyo University of Agriculture and Technology, 7.Muroran Institute of Technology, 8.Hiroshima University, 9.Kanazawa University, 10.National Institute for Environmental Studies)
Keywords:aerial observation, nitrate, total odd nitrogen species, East Asia
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.