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首页> 外文期刊>Atmospheric chemistry and physics >Sulfate-nitrate-ammonium aerosols over China: Response to 2000-2015 emission changes of sulfur dioxide, nitrogen oxides, and ammonia
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Sulfate-nitrate-ammonium aerosols over China: Response to 2000-2015 emission changes of sulfur dioxide, nitrogen oxides, and ammonia

机译:中国各地的硫酸盐-硝酸盐-铵气溶胶:对2000-2015年二氧化硫,氮氧化物和氨气排放变化的响应

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摘要

We use a chemical transport model to examine the change of sulfate-nitrate-ammonium (SNA) aerosols over China due to anthropogenic emission changes of their precursors (SO_2, NO_x and NH_3) from 2000 to 2015. From 2000 to 2006, annual mean SNA concentrations increased by about 60% over China as a result of the 60% and 80% increases in SO _2 and NO_x emissions. During this period, sulfate is the dominant component of SNA over South China (SC) and Sichuan Basin (SCB), while nitrate and sulfate contribute equally over North China (NC). Based on emission reduction targets in the 12th (2011-2015) Five-Year Plan (FYP), China's total SO_2 and NO_x emissions are projected to change by -16% and +16% from 2006 to 2015, respectively. The amount of NH3 emissions in 2015 is uncertain, given the lack of sufficient information on the past and present levels of NH3 emissions in China. With no change in NH3 emissions, SNA mass concentrations in 2015 will decrease over SCB and SC compared to their 2006 levels, but increase over NC where the magnitude of nitrate increase exceeds that of sulfate reduction. This suggests that the SO_2 emission reduction target set by the 12th FYP, although effective in reducing SNA over SC and SCB, will not be successful over NC, for which NO_x emission control needs to be strengthened. If NH3 emissions are allowed to keep their recent growth rate and increase by +16% from 2006 to 2015, the benefit of SO_2 reduction will be completely offset over all of China due to the significant increase of nitrate, demonstrating the critical role of NH_3 in regulating nitrate. The effective strategy to control SNA and hence PM_(2.5) pollution over China should thus be based on improving understanding of current NH_3 emissions and putting more emphasis on controlling NH_3 emissions in the future.
机译:我们使用化学迁移模型研究了2000年至2015年由于其前体(SO_2,NO_x和NH_3)的人为排放变化而导致的中国硫酸盐-硝酸盐-铵(SNA)气溶胶的变化。从2000年至2006年,SNA的年均平均值由于SO _2和NO_x排放量分别增加60%和80%,中国的污染物浓度比中国增加了约60%。在此期间,硫酸盐是华南(SC)和四川盆地(SCB)的SNA的主要组成部分,而硝酸盐和硫酸盐在华北(NC)的贡献均等。根据第十二个(2011-2015年)五年计划的减排目标,从2006年到2015年,中国的SO_2和NO_x排放总量预计分别变化-16%和+ 16%。由于缺乏有关中国过去和现在的NH3排放水平的足够信息,2015年的NH3排放量尚不确定。在不改变NH3排放的情况下,相比于2006年的水平,SCB和SC的SNA质量浓度将在2015年降低,但在NC的水平有所增加,因为硝酸盐的增加幅度超过硫酸盐的减少幅度。这表明“十二五”规划设定的SO_2减排目标虽然可以有效地降低SC和SCB的SNA,但在NC方面将无法成功,为此需要加强NO_x的排放控制。如果允许NH3排放保持其最近的增长率并在2006年至2015年期间增加+ 16%,那么由于硝酸盐的大量增加,SO_2减排的收益将在整个中国被完全抵消,这表明NH_3的关键作用调节硝酸盐。因此,控制中国国民账户体系以及由此引起的PM_(2.5)污染的有效策略应基于对当前NH_3排放的了解,并在未来更加重视控制NH_3排放。

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