Atmospheric Chemistry and Physics (Nov 2015)

Quantifying atmospheric nitrogen deposition through a nationwide monitoring network across China

  • W. Xu,
  • X. S. Luo,
  • Y. P. Pan,
  • L. Zhang,
  • A. H. Tang,
  • J. L. Shen,
  • Y. Zhang,
  • K. H. Li,
  • Q. H. Wu,
  • D. W. Yang,
  • Y. Y. Zhang,
  • J. Xue,
  • W. Q. Li,
  • Q. Q. Li,
  • L. Tang,
  • S. H. Lu,
  • T. Liang,
  • Y. A. Tong,
  • P. Liu,
  • Q. Zhang,
  • Z. Q. Xiong,
  • X. J. Shi,
  • L. H. Wu,
  • W. Q. Shi,
  • K. Tian,
  • X. H. Zhong,
  • K. Shi,
  • Q. Y. Tang,
  • L. J. Zhang,
  • J. L. Huang,
  • C. E. He,
  • F. H. Kuang,
  • B. Zhu,
  • H. Liu,
  • X. Jin,
  • Y. J. Xin,
  • X. K. Shi,
  • E. Z. Du,
  • A. J. Dore,
  • S. Tang,
  • J. L. Collett Jr.,
  • K. Goulding,
  • Y. X. Sun,
  • J. Ren,
  • F. S. Zhang,
  • X. J. Liu

DOI
https://doi.org/10.5194/acp-15-12345-2015
Journal volume & issue
Vol. 15, no. 21
pp. 12345 – 12360

Abstract

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A Nationwide Nitrogen Deposition Monitoring Network (NNDMN) containing 43 monitoring sites was established in China to measure gaseous NH3, NO2, and HNO3 and particulate NH4+ and NO3− in air and/or precipitation from 2010 to 2014. Wet/bulk deposition fluxes of Nr species were collected by precipitation gauge method and measured by continuous-flow analyzer; dry deposition fluxes were estimated using airborne concentration measurements and inferential models. Our observations reveal large spatial variations of atmospheric Nr concentrations and dry and wet/bulk Nr deposition. On a national basis, the annual average concentrations (1.3–47.0 μg N m−3) and dry plus wet/bulk deposition fluxes (2.9–83.3 kg N ha−1 yr−1) of inorganic Nr species are ranked by land use as urban > rural > background sites and by regions as north China > southeast China > southwest China > northeast China > northwest China > Tibetan Plateau, reflecting the impact of anthropogenic Nr emission. Average dry and wet/bulk N deposition fluxes were 20.6 ± 11.2 (mean ± standard deviation) and 19.3 ± 9.2 kg N ha−1 yr−1 across China, with reduced N deposition dominating both dry and wet/bulk deposition. Our results suggest atmospheric dry N deposition is equally important to wet/bulk N deposition at the national scale. Therefore, both deposition forms should be included when considering the impacts of N deposition on environment and ecosystem health.