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Water-soluble organic nitrogen in the aerosols and rainwater at an urban site in Japan: Implications for the nitrogen composition in the atmospheric deposition

机译:日本城市地区气溶胶和雨水中的水溶性有机氮:对大气沉积中氮成分的影响

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Simultaneous measurements of the water-soluble organic nitrogen (WSON) in the aerosols and rainwater were conducted to clarify the deposition pathway of the atmospheric WSON. In the aerosols, about 10% of the water-soluble total nitrogen (WSTN) was in an organic form, and a large portion (about 81% on average) of the WSON was distributed in the fine-mode range. Concentrations of the fine-mode WSON were associated with the acidity of the fine particles, suggesting the secondary production of the WSON in the acid fine particles. On the other hand, it was suggested that the coarse-mode WSON was derived from bio-particles, such as plant debris, although its concentrations were low and widely scattered. Dry deposition amounts of the WSON estimated from the concentrations and dry deposition velocities of the particulate WSON suggested that almost all of the dry deposition of the particulate WSON was derived from the coarse-mode particles. The contribution of the fine-mode particles to the dry deposition was negligible. About 10% of the WSTN in the bulk precipitation was in an organic form. The bulk deposition amounts of the WSON were largely dependent on the rainfall amounts and coarse-mode WSON concentrations. Although about 30% of the WSON in the bulk deposition was from the dry deposition, the wet deposition significantly contributed to the WSON deposition, especially in the rainy season. Wet deposition is the major removal process of WSON from spring to autumn; however, in winter, dry and wet deposition are comparable.
机译:同时测量了气溶胶和雨水中的水溶性有机氮(WSON),以阐明大气WSON的沉积途径。在气溶胶中,约有10%的水溶性总氮(WSTN)是有机形式,而大部分(平均约81%)的WSON分布在精细模式范围内。精细模式WSON的浓度与微粒的酸度相关,表明在酸性微粒中WSON的二次生成。另一方面,建议粗模式WSON来自生物颗粒,例如植物碎片,尽管其浓度较低且分散很广。由颗粒WSON的浓度和干沉积速度估计的WSON的干沉积量表明,颗粒WSON的几乎所有干沉积均来自粗模式颗粒。细模颗粒对干法沉积的贡献可忽略不计。整体沉淀中约10%的WSTN是有机形式。 WSON的整体沉积量在很大程度上取决于降雨量和粗模式WSON浓度。尽管整体沉积中WSON的约30%来自干沉降,但湿沉降显着促进了WSON沉积,尤其是在雨季。从春季到秋季,湿沉降是WSON的主要去除过程。但是,在冬季,干沉降和湿沉降是可比的。

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