Chloride (HCl ∕ Cl−) dominates inorganic aerosol formation from ammonia in the Indo-Gangetic Plain during winter: modeling and comparison with observations

Abstract. The Winter Fog Experiment (WiFEX) was an intensive field campaign conducted at Indira Gandhi International Airport (IGIA) Delhi, India, in the Indo-Gangetic Plain (IGP) during the winter of 2017–2018. Here, we report the first comparison in South Asia of high-temporal-resolution simulation of ammonia (NH3) along with ammonium (NH4+) and total NHx (i.e., NH3+ NH4+) using the Weather Research and Forecasting model coupled with chemistry (WRF-Chem) and measurements made using the Monitor for AeRosols and Gases in Ambient Air (MARGA) at the WiFEX research site. In the present study, we incorporated the Model for Simulating Aerosol Interactions and Chemistry (MOSAIC) aerosol scheme into WRF-Chem. Despite simulated total NHx values and variability often agreeing well with the observations, the model frequently simulated higher NH3 and lower NH4+ concentrations than the observations. Under the winter conditions of high relative humidity (RH) in Delhi, hydrogen chloride (HCl) was found to promote the increase in the particle fraction of NH4+ (which accounted for 49.5 % of the resolved aerosol in equivalent units), with chloride (Cl−) (29.7 %) as the primary anion. By contrast, the absence of chloride (HCl / Cl−) chemistry in the standard WRF-Chem model results in the prediction of sulfate (SO42-) as the dominant inorganic aerosol anion. To understand the mismatch associated with the fraction of NHx in the particulate phase (NH4+ / NHx), we added HCl / Cl− to the model and evaluated the influence of its chemistry by conducting three sensitivity experiments using the model: no HCl, base case HCl (using a published waste burning inventory), and 3 × base HCl run. We found that 3 × base HCl increased the simulated average NH4+ by 13.1 µg m−3 and NHx by 9.8 µg m−3 concentration while reducing the average NH3 by 3.2 µg m−3, which is more in accord with the measurements. Thus HCl / Cl− chemistry in the model increases total NHx concentration, which was further demonstrated by reducing NH3 emissions by a factor of 3 (−3 × NH3_EMI) in the 3 × base HCl simulation. Reducing NH3 emissions in the 3 × base HCl simulation successfully addressed the discrepancy between measured and modeled total NHx. We conclude that modeling the fate of NH3 in Delhi requires a correct chemistry mechanism accounting for chloride dynamics with accurate inventories of both NH3 and HCl emissions.

[1]  Jianjun He,et al.  Ammonium Chloride Associated Aerosol Liquid Water Enhances Haze in Delhi, India , 2022, Environmental science & technology.

[2]  R. Nanjundiah,et al.  New Delhi: air-quality warning system cuts peak pollution , 2022, Nature.

[3]  C. Jena,et al.  Nationwide CoViD-19 lockdown impact on air quality in India , 2022, MAUSAM.

[4]  M. Rajeevan,et al.  Enhanced secondary aerosol formation driven by excess ammonia during fog episodes in Delhi, India. , 2021, Chemosphere.

[5]  Sneha Saha,et al.  Underreporting and open burning – the two largest challenges for sustainable waste management in India , 2021 .

[6]  R. Van Dingenen,et al.  Abating ammonia is more cost-effective than nitrogen oxides for mitigating PM2.5 air pollution , 2021, Science.

[7]  Lin Peng,et al.  Role of ammonia in secondary inorganic aerosols formation at an ammonia-rich city in winter in north China: A comparative study among industry, urban, and rural sites. , 2021, Environmental pollution.

[8]  F. Bowman,et al.  WRF-Chem Modeling of Summertime Air Pollution in the Northern Great Plains: Chemistry and Aerosol Mechanism Intercomparison , 2021, Atmosphere.

[9]  S. Ghude,et al.  Probing wintertime air pollution sources in the Indo-Gangetic Plain through 52 hydrocarbons measured rarely at Delhi & Mohali. , 2021, The Science of the total environment.

[10]  S. Ghude,et al.  Study of ice nucleating particles in fog-haze weather at New Delhi, India: A case of polluted environment , 2021 .

[11]  Weili Lin,et al.  Measurement report: Exploring NH3 behavior in urban and suburban Beijing: comparison and implications , 2021 .

[12]  S. K. Sinha,et al.  Nitrogen Challenges and Opportunities for Agricultural and Environmental Science in India , 2021, Frontiers in Sustainable Food Systems.

[13]  G. Beig,et al.  Performance of high resolution (400 m) PM2.5 forecast over Delhi , 2021, Scientific Reports.

[14]  S. Martin,et al.  Enhanced aerosol particle growth sustained by high continental chlorine emission in India , 2021, Nature Geoscience.

[15]  T. Gupta,et al.  Chemical characterization and stable nitrogen isotope composition of nitrogenous component of ambient aerosols from Kanpur in the Indo-Gangetic Plains. , 2020, The Science of the total environment.

[16]  C. Clerbaux,et al.  Record high levels of atmospheric ammonia over India: Spatial and temporal analyses. , 2020, The Science of the total environment.

[17]  P. Levy,et al.  Alkaline air: changing perspectives on nitrogen and air pollution in an ammonia-rich world , 2020, Philosophical Transactions of the Royal Society A.

[18]  F. Yu,et al.  Quantification of Atmospheric Ammonia Concentrations: A Review of Its Measurement and Modeling , 2020, Atmosphere.

[19]  T. Adhya,et al.  Analysis of atmospheric ammonia over South and East Asia based on the MOZART-4 model and its comparison with satellite and surface observations , 2020, Atmospheric Chemistry and Physics.

[20]  Yu Song,et al.  Why is the Indo-Gangetic Plain the region with the largest NH3 column in the globe during pre-monsoon and monsoon seasons? , 2020 .

[21]  Yanfen Lin,et al.  Importance of gas-particle partitioning of ammonia in haze formation in the rural agricultural environment , 2020, Atmospheric Chemistry and Physics.

[22]  S. Alessandrini,et al.  Evaluation of PM2.5 Forecast using Chemical Data Assimilation in the WRF-Chem Model: A Novel Initiative Under the Ministry of Earth Sciences Air Quality Early Warning System for Delhi, India , 2020, Current Science.

[23]  Y. Miao,et al.  Regional Transport Increases Ammonia Concentration in Beijing, China , 2020, Atmosphere.

[24]  M. Rajeevan,et al.  Characterization of atmospheric trace gases and water soluble inorganic chemical ions of PM1 and PM2.5 at Indira Gandhi International Airport, New Delhi during 2017-18 winter. , 2020, The Science of the total environment.

[25]  R. Kumar,et al.  How much large scale crop residue burning affect the air quality in Delhi? , 2020, Environmental science & technology.

[26]  Yi Liu,et al.  Satellite-Observed Variations and Trends in Carbon Monoxide over Asia and Their Sensitivities to Biomass Burning , 2020, Remote. Sens..

[27]  S. Sharma,et al.  Spatial Variability and Sources of Atmospheric Ammonia in India: A Review , 2020, Aerosol Science and Engineering.

[28]  F. Cao,et al.  Aerosol chemical component: Simulations with WRF-Chem and comparison with observations in Nanjing , 2019 .

[29]  A. Russell,et al.  Aerosol pH and liquid water content determine when particulate matter is sensitive to ammonia and nitrate availability , 2019, Atmospheric Chemistry and Physics.

[30]  Pallavi,et al.  Gridded Emissions of CO, NO x, SO2, CO2, NH3, HCl, CH4, PM2.5, PM10, BC, and NMVOC from Open Municipal Waste Burning in India. , 2019, Environmental science & technology.

[31]  M. Rajeevan,et al.  Characterization and source identification of PM2.5 and its chemical and carbonaceous constituents during Winter Fog Experiment 2015-16 at Indira Gandhi International Airport, Delhi. , 2019, The Science of the total environment.

[32]  H. Herrmann,et al.  Development of an online-coupled MARGA upgrade for the 2 h interval quantification of low-molecular-weight organic acids in the gas and particle phases , 2019, Atmospheric Measurement Techniques.

[33]  M. Sutton,et al.  Satellite pinpoints ammonia sources globally , 2018, Nature.

[34]  C. Clerbaux,et al.  Industrial and agricultural ammonia point sources exposed , 2018, Nature.

[35]  Saraswati,et al.  Simultaneous Measurements of Ambient NH3 and Its Relationship with Other Trace Gases, PM2.5 and Meteorological Parameters over Delhi, India , 2018, MAPAN.

[36]  George K. Georgiou,et al.  Air quality modelling in the summer over the eastern Mediterranean using WRF-Chem: chemistry and aerosol mechanism intercomparison , 2017, Atmospheric Chemistry and Physics.

[37]  Xiaobin Xu,et al.  Role of ambient ammonia in particulate ammonium formation at a rural site in the North China Plain , 2017 .

[38]  Atul Srivastava,et al.  Winter fog experiment over the Indo-Gangetic plains of India , 2017 .

[39]  J. Collett,et al.  The role of dew as a night-time reservoir and morning source for atmospheric ammonia , 2016 .

[40]  C. Bretherton,et al.  Improving our fundamental understanding of the role of aerosol−cloud interactions in the climate system , 2016, Proceedings of the National Academy of Sciences.

[41]  Manju Mohan,et al.  Validation of WRF/Chem model and sensitivity of chemical mechanisms to ozone simulation over megacity Delhi , 2015 .

[42]  Song Gao,et al.  Atmospheric ammonia and its impacts on regional air quality over the megacity of Shanghai, China , 2015, Scientific Reports.

[43]  C. Braban,et al.  Water soluble aerosols and gases at a UK background site – Part 1: Controls of PM 2.5 and PM 10 aerosol composition , 2015 .

[44]  J. Murphy,et al.  Soil–atmosphere exchange of ammonia in a non-fertilized grassland: measured emission potentials and inferred fluxes , 2014 .

[45]  A. Hodzic,et al.  The effect of dry and wet deposition of condensable vapors on secondary organic aerosols concentrations over the continental US , 2014 .

[46]  H. Pathak,et al.  Ammonia Emission from Rice–Wheat Cropping System in Subtropical Soil of India , 2014, Agricultural Research.

[47]  Saraswati,et al.  Characteristics of ambient ammonia over Delhi, India , 2014, Meteorology and Atmospheric Physics.

[48]  Rajasekhar Balasubramanian,et al.  Ammonia in the atmosphere: a review on emission sources, atmospheric chemistry and deposition on terrestrial bodies , 2013, Environmental Science and Pollution Research.

[49]  Stefan Reis,et al.  Towards a climate-dependent paradigm of ammonia emission and deposition , 2013, Philosophical Transactions of the Royal Society B: Biological Sciences.

[50]  F. Kelliher,et al.  Ammonia emissions from cattle urine and dung excreted on pasture , 2013 .

[51]  T. K. Mandal,et al.  Ammonia emission from subtropical crop land area in India , 2012, Asia-Pacific Journal of Atmospheric Sciences.

[52]  Pasi Aalto,et al.  Semi-continuous gas and inorganic aerosol measurements at a Finnish urban site: comparisons with filters, nitrogen in aerosol and gas phases, and aerosol acidity , 2012 .

[53]  Min Hu,et al.  Chemical characteristics of inorganic ammonium salts in PM 2.5 in the atmosphere of Beijing (China) , 2011 .

[54]  T. Zhu,et al.  Occurrence of gas phase ammonia in the area of Beijing (China) , 2010 .

[55]  J. Brook,et al.  The influence of gas-particle partitioning and surface-atmosphere exchange on ammonia during BAQS-Met , 2010 .

[56]  J. Schjoerring,et al.  Dynamics of ammonia exchange with cut grassland: synthesis of results and conclusions of the GRAMINAE Integrated Experiment , 2009 .

[57]  Lieven Clarisse,et al.  Global ammonia distribution derived from infrared satellite observations , 2009 .

[58]  G. Beig,et al.  Satellite derived trends in NO2 over the major global hotspot regions during the past decade and their inter-comparison. , 2009, Environmental pollution.

[59]  R. Otjes,et al.  An automated analyzer to measure surface-atmosphere exchange fluxes of water soluble inorganic aerosol compounds and reactive trace gases. , 2009, Environmental science & technology.

[60]  F. Dentener,et al.  Ammonia in the environment: from ancient times to the present. , 2008, Environmental pollution.

[61]  B. C. Arya,et al.  Ozone in ambient air at a tropical megacity, Delhi: characteristics, trends and cumulative ozone exposure indices , 2008 .

[62]  Peter J Adams,et al.  Ammonia emission controls as a cost-effective strategy for reducing atmospheric particulate matter in the Eastern United States. , 2007, Environmental science & technology.

[63]  S. Freitas,et al.  Including the sub-grid scale plume rise of vegetation fires in low resolution atmospheric transport models , 2006 .

[64]  P. Palmer,et al.  Estimates of global terrestrial isoprene emissions using MEGAN (Model of Emissions of Gases and Aerosols from Nature) , 2006 .

[65]  J. Lelieveld,et al.  Importance of mineral cations and organics in gas-aerosol partitioning of reactive nitrogen compounds : case study based on MINOS results , 2005 .

[66]  J. Seinfeld,et al.  Atmospheric Chemistry and Physics: From Air Pollution to Climate Change , 1998 .

[67]  A. Leytem,et al.  Ammonia emissions from dairy lagoons in the western U.S. , 2018 .

[68]  Shi-chang Kang,et al.  Sensitivity Analysis of Chemical Mechanisms in the WRF-Chem Model in Reconstructing Aerosol Concentrations and Optical Properties in the Tibetan Plateau , 2017 .

[69]  Jaiprakash,et al.  Chemical characterization of PM1.0 aerosol in Delhi and source apportionment using positive matrix factorization , 2016, Environmental Science and Pollution Research.

[70]  Louisa Emmons,et al.  Satellite constraints of nitrogen oxide (NOx) emissions from India based on OMI observations and WRF‐Chem simulations , 2012 .

[71]  Karl Ropkins,et al.  openair - An R package for air quality data analysis , 2012, Environ. Model. Softw..