Nitrate transboundary heavy pollution over East Asia in winter

High PM<sub>2. 5</sub> concentrations of around 100 µg m<sup>−3</sup> were observed twice during an intensive observation campaign in January 2015 at Fukuoka (33.52° N, 130.47° E) in western Japan. These events were analyzed comprehensively with a regional chemical transport...

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Main Authors: S. Itahashi, I. Uno, K. Osada, Y. Kamiguchi, S. Yamamoto, K. Tamura, Z. Wang, Y. Kurosaki, Y. Kanaya
Format: Article
Language:English
Published: Copernicus Publications 2017-03-01
Series:Atmospheric Chemistry and Physics
Online Access:http://www.atmos-chem-phys.net/17/3823/2017/acp-17-3823-2017.pdf
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author S. Itahashi
I. Uno
K. Osada
Y. Kamiguchi
S. Yamamoto
K. Tamura
Z. Wang
Y. Kurosaki
Y. Kanaya
spellingShingle S. Itahashi
I. Uno
K. Osada
Y. Kamiguchi
S. Yamamoto
K. Tamura
Z. Wang
Y. Kurosaki
Y. Kanaya
Nitrate transboundary heavy pollution over East Asia in winter
Atmospheric Chemistry and Physics
author_facet S. Itahashi
I. Uno
K. Osada
Y. Kamiguchi
S. Yamamoto
K. Tamura
Z. Wang
Y. Kurosaki
Y. Kanaya
author_sort S. Itahashi
title Nitrate transboundary heavy pollution over East Asia in winter
title_short Nitrate transboundary heavy pollution over East Asia in winter
title_full Nitrate transboundary heavy pollution over East Asia in winter
title_fullStr Nitrate transboundary heavy pollution over East Asia in winter
title_full_unstemmed Nitrate transboundary heavy pollution over East Asia in winter
title_sort nitrate transboundary heavy pollution over east asia in winter
publisher Copernicus Publications
series Atmospheric Chemistry and Physics
issn 1680-7316
1680-7324
publishDate 2017-03-01
description High PM<sub>2. 5</sub> concentrations of around 100 µg m<sup>−3</sup> were observed twice during an intensive observation campaign in January 2015 at Fukuoka (33.52° N, 130.47° E) in western Japan. These events were analyzed comprehensively with a regional chemical transport model and synergetic ground-based observations with state-of-the-art measurement systems, which can capture the behavior of secondary inorganic aerosols (SO<sub>4</sub><sup>2−</sup>, NO<sub>3</sub><sup>−</sup>, and NH<sub>4</sub><sup>+</sup>). The first episode of high PM<sub>2. 5</sub> concentration was dominated by NO<sub>3</sub><sup>−</sup> (type N) and the second episode by SO<sub>4</sub><sup>2−</sup> (type S). The concentration of NH<sub>4</sub><sup>+</sup> (the counterion for SO<sub>4</sub><sup>2−</sup> and NO<sub>3</sub><sup>−</sup>) was high for both types. A sensitivity simulation in the chemical transport model showed that the dominant contribution was from transboundary air pollution for both types. To investigate the differences between these types further, the chemical transport model results were examined, and a backward trajectory analysis was used to provide additional information. During both types of episodes, high concentrations of NO<sub>3</sub><sup>−</sup> were found above China, and an air mass that originated from northeast China reached Fukuoka. The travel time from the coastline of China to Fukuoka differed between types: it was 18 h for type N and 24 h for type S. The conversion ratio of SO<sub>2</sub> to SO<sub>4</sub><sup>2−</sup> (<i>F</i><sub>s</sub>) was less than 0.1 for type N, but reached 0.3 for type S as the air mass approached Fukuoka. The higher <i>F</i><sub>s</sub> for type S was related to the higher relative humidity and the concentration of HO<sub>2</sub>, which produces H<sub>2</sub>O<sub>2</sub>, the most effective oxidant for the aqueous-phase production of SO<sub>4</sub><sup>2−</sup>. Analyzing the gas ratio as an indicator of the sensitivity of NO<sub>3</sub><sup>−</sup> to changes in SO<sub>4</sub><sup>2−</sup> and NH<sub>4</sub><sup>+</sup> showed that the air mass over China was NH<sub>3</sub>-rich for type N, but almost NH<sub>3</sub>-neutral for type S. Thus, although the high concentration of NO<sub>3</sub><sup>−</sup> above China gradually decreased during transport from China to Fukuoka, higher NO<sub>3</sub><sup>−</sup> concentrations were maintained during transport owing to the lower SO<sub>4</sub><sup>2−</sup> for type N. In contrast, for type S, the production of SO<sub>4</sub><sup>2−</sup> led to the decomposition of NH<sub>4</sub>NO<sub>3</sub>, and more SO<sub>4</sub><sup>2−</sup> was transported. Notably, the type N transport pattern was limited to western Japan, especially the island of Kyushu. Transboundary air pollution dominated by SO<sub>4</sub><sup>2−</sup> (type S) has been recognized as a major pattern of pollution over East Asia. However, our study confirms the importance of transboundary air pollution dominated by NO<sub>3</sub><sup>−</sup>, which will help refine our understanding of transboundary heavy PM<sub>2. 5</sub> pollution in winter over East Asia.
url http://www.atmos-chem-phys.net/17/3823/2017/acp-17-3823-2017.pdf
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spelling doaj-2af32d7c2c1e410c8dfb6445d32348602020-11-25T00:52:30ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242017-03-011763823384310.5194/acp-17-3823-2017Nitrate transboundary heavy pollution over East Asia in winterS. Itahashi0I. Uno1K. Osada2Y. Kamiguchi3S. Yamamoto4K. Tamura5Z. Wang6Y. Kurosaki7Y. Kanaya8Environmental Science Research Laboratory, Central Research Institute of Electric Power Industry, 1646 Abiko, Abiko-shi, Chiba 270-1194, JapanResearch Institute for Applied Mechanics, Kyushu University, 6-1 Kasuga Park, Kasuga, Fukuoka 816-8580, JapanGraduate School of Environmental Studies, Nagoya University, D2-1 (510) Furo-cho, Chikusa-ku, Nagoya, Aichi 464-8601, JapanGraduate School of Environmental Studies, Nagoya University, D2-1 (510) Furo-cho, Chikusa-ku, Nagoya, Aichi 464-8601, JapanFukuoka Institute of Health and Environmental Sciences, 39 Mukaizano, Dazaifu-shi, Fukuoka 818-0135, JapanNagasaki Prefectural Environmental Affairs Department, 2-1306-11 Ikeda, Omura, Nagasaki 856-0026, JapanResearch Institute for Applied Mechanics, Kyushu University, 6-1 Kasuga Park, Kasuga, Fukuoka 816-8580, JapanArid Land Research Center, Tottori University, 1390 Hamasaka, Tottori 680-0001, JapanJapan Agency for Marine-Earth Science and Technology, 3173-25 Showa-machi, Kanazawa-ku, Yokohama, Kanagawa 236-0001, JapanHigh PM<sub>2. 5</sub> concentrations of around 100 µg m<sup>−3</sup> were observed twice during an intensive observation campaign in January 2015 at Fukuoka (33.52° N, 130.47° E) in western Japan. These events were analyzed comprehensively with a regional chemical transport model and synergetic ground-based observations with state-of-the-art measurement systems, which can capture the behavior of secondary inorganic aerosols (SO<sub>4</sub><sup>2−</sup>, NO<sub>3</sub><sup>−</sup>, and NH<sub>4</sub><sup>+</sup>). The first episode of high PM<sub>2. 5</sub> concentration was dominated by NO<sub>3</sub><sup>−</sup> (type N) and the second episode by SO<sub>4</sub><sup>2−</sup> (type S). The concentration of NH<sub>4</sub><sup>+</sup> (the counterion for SO<sub>4</sub><sup>2−</sup> and NO<sub>3</sub><sup>−</sup>) was high for both types. A sensitivity simulation in the chemical transport model showed that the dominant contribution was from transboundary air pollution for both types. To investigate the differences between these types further, the chemical transport model results were examined, and a backward trajectory analysis was used to provide additional information. During both types of episodes, high concentrations of NO<sub>3</sub><sup>−</sup> were found above China, and an air mass that originated from northeast China reached Fukuoka. The travel time from the coastline of China to Fukuoka differed between types: it was 18 h for type N and 24 h for type S. The conversion ratio of SO<sub>2</sub> to SO<sub>4</sub><sup>2−</sup> (<i>F</i><sub>s</sub>) was less than 0.1 for type N, but reached 0.3 for type S as the air mass approached Fukuoka. The higher <i>F</i><sub>s</sub> for type S was related to the higher relative humidity and the concentration of HO<sub>2</sub>, which produces H<sub>2</sub>O<sub>2</sub>, the most effective oxidant for the aqueous-phase production of SO<sub>4</sub><sup>2−</sup>. Analyzing the gas ratio as an indicator of the sensitivity of NO<sub>3</sub><sup>−</sup> to changes in SO<sub>4</sub><sup>2−</sup> and NH<sub>4</sub><sup>+</sup> showed that the air mass over China was NH<sub>3</sub>-rich for type N, but almost NH<sub>3</sub>-neutral for type S. Thus, although the high concentration of NO<sub>3</sub><sup>−</sup> above China gradually decreased during transport from China to Fukuoka, higher NO<sub>3</sub><sup>−</sup> concentrations were maintained during transport owing to the lower SO<sub>4</sub><sup>2−</sup> for type N. In contrast, for type S, the production of SO<sub>4</sub><sup>2−</sup> led to the decomposition of NH<sub>4</sub>NO<sub>3</sub>, and more SO<sub>4</sub><sup>2−</sup> was transported. Notably, the type N transport pattern was limited to western Japan, especially the island of Kyushu. Transboundary air pollution dominated by SO<sub>4</sub><sup>2−</sup> (type S) has been recognized as a major pattern of pollution over East Asia. However, our study confirms the importance of transboundary air pollution dominated by NO<sub>3</sub><sup>−</sup>, which will help refine our understanding of transboundary heavy PM<sub>2. 5</sub> pollution in winter over East Asia.http://www.atmos-chem-phys.net/17/3823/2017/acp-17-3823-2017.pdf