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Chinese Journal of Applied Ecology ›› 2019, Vol. 30 ›› Issue (10): 3285-3291.doi: 10.13287/j.1001-9332.201910.022

• Special Features of the 11th National Symposium on Young Ecologists • Previous Articles     Next Articles

Soil acidification induced by nitrogen addition and its responses to water addition in Inner Mongolia Temperate Steppe, China

GUO Qun1,2*   

  1. 1Key Laboratory of Ecosystem Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China;
    2College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100190, China
  • Received:2019-04-03 Online:2019-10-20 Published:2019-10-20
  • Contact: *E-mail: guoq@igsnrr.ac.cn
  • Supported by:
    This work was supported by the National Natural Science Foundation of China (31570437), the Strategic Priority Research Program of the Chinese Academy of Sciences (XDA23060205) and the National Key R&D Program of China (2017YFA0604801).

Abstract: Soil acidification due to exogenous nitrogen (N) deposition has been received sufficient attention in the past several decades. Whether the N-induced soil acidification is modulated by the altering precipitation regimes remains unclear. In this study, based on a five-year (2013-2017) manipulative field experiment with factorial N addition (10 and 40 g N·m-2·a-1 ) and water addition (a total amount of 80 mm·a-1 was added in terms of five intensities, i.e., 2 mm×40 times, 5 mm×16 times, 10 mm×8 times, 20 mm×4 times, and 40 mm×2 times) in a typical steppe in Inner Mongolia, I analyzed the effects of water addition on soil acidification induced by N addition. I found that soil acidification induced by 40 g N m-2·a-1 N addition occurred earlier, more significant, and with a greater year by year changed rate than that of 10 g N·m-2·a-1 N addition. After one year treatment, I observed significant soil acidification at soil profiles of 0-5, 5-10, and 10-20 cm in the treatment of 40 g N·m-2·a-1 N addition, while significant soil acidification in 10 g N·m-2·a-1 N addition was observed after 1, 4, and 5 year since N was added for the three layers, respectively. In general, the magnitude of soil acidification induced by N addition increased with the increasing period after N addition, and the slope of the regression line was steeper in the relatively higher dose of N addition (40 g N·m-2·a-1). Soil acidification induced by N addition could not be reversed by water addition, but water addition in terms of relatively lower intensities (i.e., all the treatments except 40 mm×2 times) could relieve the N-induced soil acidification to a certain extent in the treatment with lower dose of N addition (10 g N·m-2·a-1) in dry years. In wet years, however, water addition exacerbated soil acidification after N was added, especially in the topsoil. The leaching of soil inorganic N after higher intensity of water addition (10-40 mm) could explain the deteriorated N-induced soil acidification when water was added. There was no significance for the relief or deterioration to N-induced soil acidification by water addition. Our results had important implications for understanding grassland responses to N deposition and altered precipi-tation regime in the future.