Ammonia emission control in China would mitigate haze pollution and nitrogen deposition, but worsen acid rain

Significance Atmospheric ammonia plays important roles in fine particle pollution, acid rain, and nitrogen deposition. China, known as the world’s top emitter of gaseous ammonia, plans to control ammonia emissions to mitigate the haze pollution that has recently emerged. However, the complex side effects are still unclear. By integrating a chemical transport model, nationwide measurements, and a sophisticated ammonia emission model, we find that ammonia emission control would significantly aggravate acid rain pollution, thereby offsetting the benefit from reduced fine particle pollution and nitrogen deposition. Our work suggests that region-specific ammonia-control strategies provide a more rational and effective way to achieve the dual benefits of protecting human and ecosystem health in China. China has been experiencing fine particle (i.e., aerodynamic diameters ≤ 2.5 µm; PM2.5) pollution and acid rain in recent decades, which exert adverse impacts on human health and the ecosystem. Recently, ammonia (i.e., NH3) emission reduction has been proposed as a strategic option to mitigate haze pollution. However, atmospheric NH3 is also closely bound to nitrogen deposition and acid rain, and comprehensive impacts of NH3 emission control are still poorly understood in China. In this study, by integrating a chemical transport model with a high-resolution NH3 emission inventory, we find that NH3 emission abatement can mitigate PM2.5 pollution and nitrogen deposition but would worsen acid rain in China. Quantitatively, a 50% reduction in NH3 emissions achievable by improving agricultural management, along with a targeted emission reduction (15%) for sulfur dioxide and nitrogen oxides, can alleviate PM2.5 pollution by 11−17% primarily by suppressing ammonium nitrate formation. Meanwhile, nitrogen deposition is estimated to decrease by 34%, with the area exceeding the critical load shrinking from 17% to 9% of China’s terrestrial land. Nevertheless, this NH3 reduction would significantly aggravate precipitation acidification, with a decrease of as much as 1.0 unit in rainfall pH and a corresponding substantial increase in areas with heavy acid rain. An economic evaluation demonstrates that the worsened acid rain would partly offset the total economic benefit from improved air quality and less nitrogen deposition. After considering the costs of abatement options, we propose a region-specific strategy for multipollutant controls that will benefit human and ecosystem health.

[1]  Ke Li,et al.  Quantifying atmospheric nitrogen deposition through a nationwide monitoring network across China , 2015 .

[2]  Renjian Zhang,et al.  New insights into PM 2.5 chemical composition and sources in two major cities in China during extreme haze events using aerosol mass spectrometry , 2015 .

[3]  M. Molina,et al.  Elucidating severe urban haze formation in China , 2014, Proceedings of the National Academy of Sciences.

[4]  H. Miao,et al.  Effects of acid deposition on terrestrial ecosystems and their rehabilitation strategies in China. , 2002, Journal of environmental sciences.

[5]  David G. Streets,et al.  Sulfur dioxide emissions in China and sulfur trends in East Asia since 2000 , 2010 .

[6]  Hiroshi Hara,et al.  A global assessment of precipitation chemistry and deposition of sulfur, nitrogen, sea salt, base cations, organic acids, acidity and pH, and phosphorus , 2014 .

[7]  Julia A. Jones,et al.  Trends in cation, nitrogen, sulfate and hydrogen ion concentrations in precipitation in the United States and Europe from 1978 to 2010: a new look at an old problem , 2013, Biogeochemistry.

[8]  Xuejun Liu,et al.  Agricultural ammonia emissions in China: reconciling bottom-up and top-down estimates , 2017 .

[9]  Kebin He,et al.  Recent large reduction in sulfur dioxide emissions from Chinese power plants observed by the Ozone Monitoring Instrument , 2010 .

[10]  Qiang Zhang,et al.  Acid deposition in Asia: Emissions, deposition, and ecosystem effects , 2016 .

[11]  D. G. Streets,et al.  Sulfur dioxide emissions in China and sulfur trends in East Asia since 2000 , 2010 .

[12]  A. Russell,et al.  High aerosol acidity despite declining atmospheric sulfate concentrations over the past 15 years , 2016 .

[13]  Xin Huang,et al.  High-resolution ammonia emissions inventories in China from 1980 to 2012 , 2015 .

[14]  Xuejun Liu,et al.  Atmospheric nitrogen deposition to China: A model analysis on nitrogen budget and critical load exceedance , 2016 .

[15]  Zbigniew Klimont,et al.  Integrated Ammonia Abatement - Modelling of Emission Control Potentials and Costs in GAINS , 2011 .

[16]  Yuesi Wang,et al.  Acid neutralization of precipitation in Northern China , 2012, Journal of the Air & Waste Management Association.

[17]  Hongliang Zhang,et al.  Premature Mortality Attributable to Particulate Matter in China: Source Contributions and Responses to Reductions. , 2017, Environmental science & technology.

[18]  G. Carmichael,et al.  Acid rain and acidification in China: the importance of base cation deposition. , 2000, Environmental pollution.

[19]  J. Seinfeld,et al.  Atmospheric Chemistry and Physics: From Air Pollution to Climate Change , 1997 .

[20]  Keith Goulding,et al.  Enhanced nitrogen deposition over China , 2013, Nature.

[21]  Xin Huang,et al.  A high‐resolution ammonia emission inventory in China , 2012 .

[22]  Jun Liu,et al.  Estimating adult mortality attributable to PM2.5 exposure in China with assimilated PM2.5 concentrations based on a ground monitoring network. , 2016, The Science of the total environment.

[23]  Xiaobin Xu,et al.  Trends of the precipitation acidity over China during 1992–2006 , 2010 .

[24]  A. Piazzalunga,et al.  High secondary aerosol contribution to particulate pollution during haze events in China , 2014, Nature.

[25]  Daven K. Henze,et al.  Ammonia emissions in the United States, European Union, and China derived by high‐resolution inversion of ammonium wet deposition data: Interpretation with a new agricultural emissions inventory (MASAGE_NH3) , 2014 .

[26]  Jixi Gao,et al.  Acid rain in China. , 2006, Environmental science & technology.

[27]  Gert Jan Reinds,et al.  Critical loads of nitrogen and sulphur to avert acidification and eutrophication in Europe and China , 2014, Landscape Ecology.

[28]  W. Chan,et al.  Acid rain in southwestern China , 1988 .

[29]  Ing-Marie Gren,et al.  The European Nitrogen Assessment: Costs and benefits of nitrogen in the environment , 2011 .

[30]  Yuan Cheng,et al.  Exploring the severe winter haze in Beijing: the impact of synoptic weather, regional transport and heterogeneous reactions , 2015 .

[31]  Kebin He,et al.  Recent reduction in NOx emissions over China: synthesis of satellite observations and emission inventories , 2016 .