Response of fine particulate matter concentrations to changes of emissions and temperature in Europe

PMCAMx-2008, a three dimensional chemical transport model (CTM), was applied in Europe to quantify the changes in fine particle (PM 2.5) concentration in response to different emission reductions as well as to temperature in- crease. A summer and a winter simulation period were used, to investigate the seasonal dependence of the PM2.5 response to 50 % reductions of sulfur dioxide (SO2), ammonia (NH3), nitrogen oxides (NOx), anthropogenic volatile organic com- pounds (VOCs) and anthropogenic primary organic aerosol (POA) emissions and also to temperature increases of 2.5 and 5 K. Reduction of NH3 emissions seems to be the most effective control strategy for reducing PM2.5, in both pe- riods, resulting in a decrease of PM2.5 up to 5.1 µg m 3 and 1.8 µg m 3 (5.5 % and 4 % on average) during summer and winter respectively, mainly due to reduction of ammo- nium nitrate (NH4NO3) (20 % on average in both periods). The reduction of SO2 emissions decreases PM2.5 in both periods having a significant effect over the Balkans (up to 1.6 µg m 3 ) during the modeled summer period, mainly due to decrease of sulfate (34 % on average over the Balkans). The anthropogenic POA control strategy reduces total OA by 15 % during the modeled winter period and 8 % in the sum- mer period. The reduction of total OA is higher in urban areas close to its emissions sources. A slight decrease of OA (8 % in the modeled summer period and 4 % in the modeled win- ter period) is also predicted after a 50 % reduction of VOCs emissions due to the decrease of anthropogenic SOA. The re- duction of NOx emissions reduces PM2.5 (up to 3.4 µg m 3 ) during the summer period, due to a decrease of NH4NO3, causing although an increase of ozone concentration in ma- jor urban areas and over Western Europe. Additionally, the NOx control strategy actually increases PM2.5 levels during the winter period, due to more oxidants becoming available to react with SO2 and VOCs. The increase of temperature results in a decrease of PM2.5 in both periods over Central Europe, mainly due to a decrease of NH4NO3 during sum- mer (18 %) and fresh POA during wintertime (35 %). Signif- icant increases of OA are predicted during the summer due mainly to the increase of biogenic VOC emissions. On the contrary, OA is predicted to decrease in the modeled win- ter period due to the dominance of fresh POA reduction and the small biogenic SOA contribution to OA. The resulting in- crease of oxidant levels from the temperature rise lead to an increase of sulfate levels in both periods, mainly over North Europe and the Atlantic Ocean. The substantial reduction of PM2.5 components due to emissions reductions of their pre- cursors outlines the importance of emissions for improving air quality, while the sensitivity of PM 2.5 concentrations to temperature changes indicate that climate interactions need to be considered when predicting future levels of PM, with different net effects in different parts of Europe.

[1]  L. Fita,et al.  Seasonal dependence of WRF model biases and sensitivity to PBL schemes over Europe , 2013 .

[2]  J. Schneider,et al.  Wintertime aerosol chemical composition and source apportionment of the organic fraction in the metropolitan area of Paris , 2012 .

[3]  Francesco Canonaco,et al.  Seasonal variations in aerosol particle composition at the puy-de-Dôme research station in France , 2011 .

[4]  A.J.H. Visschedijk,et al.  General overview: European Integrated project on Aerosol Cloud Climate and Air Quality interactions (EUCAARI) - integrating aerosol research from nano to global scales , 2011 .

[5]  L. Poulain,et al.  Seasonal and diurnal variations of particulate nitrate and organic matter at the IfT research station Melpitz , 2011 .

[6]  S. Pandis,et al.  Predicted changes in summertime organic aerosol concentrations due to increased temperatures , 2011 .

[7]  Jimy Dudhia,et al.  Evaluation of WRF Parameterizations for Climate Studies over Southern Spain Using a Multistep Regionalization , 2011 .

[8]  S. Pandis,et al.  Evaluation of a three-dimensional chemical transport model (PMCAMx) in the European domain during the EUCAARI May 2008 campaign , 2011 .

[9]  R. Otjes,et al.  Aerosol chemical composition at Cabauw, the Netherlands as observed in two intensive periods in May 2008 and March 2009 , 2011 .

[10]  D. Oderbolz,et al.  Atmospheric Chemistry and Physics Aerosol Modelling in Europe with a Focus on Switzerland during Summer and Winter Episodes , 2011 .

[11]  S. Pandis,et al.  Exploring summertime organic aerosol formation in the eastern United States using a regional-scale budget approach and ambient measurements , 2010 .

[12]  D. Worsnop,et al.  Formation of highly oxygenated organic aerosol in the atmosphere: Insights from the Finokalia Aerosol Measurement Experiments , 2010 .

[13]  L. Molina,et al.  Sources and production of organic aerosol in Mexico City: insights from the combination of a chemical transport model (PMCAMx-2008) and measurements during MILAGRO , 2010 .

[14]  Ana Isabel Miranda,et al.  Climate-driven changes in air quality over Europe by the end of the 21st century, with special reference to Portugal , 2010 .

[15]  G. Leeuw,et al.  Overview of the synoptic and pollution situation over Europe during the EUCAARI-LONGREX field campaign , 2010 .

[16]  Alper Unal,et al.  Study of a winter PM episode in Istanbul using the high resolution WRF/CMAQ modeling system , 2010 .

[17]  A. Stohl,et al.  The Finokalia Aerosol Measurement Experiment – 2008 (FAME-08): an overview , 2010 .

[18]  S. Madronich,et al.  Modeling organic aerosols in a megacity: Potential contribution of semi-volatile and intermediate volatility primary organic compounds to secondary organic aerosol formation , 2010 .

[19]  P. DeCarlo,et al.  Aged organic aerosol in the Eastern Mediterranean: the Finokalia aerosol measurement experiment-2008 , 2010 .

[20]  E. Highwood,et al.  Airborne measurements of the spatial distribution of aerosol chemical composition across Europe and evolution of the organic fraction , 2010 .

[21]  L. Molina,et al.  Simulating the fine and coarse inorganic particulate matter concentrations in a polluted megacity , 2010 .

[22]  D. Ceburnis,et al.  Aerosol properties associated with air masses arriving into the North East Atlantic during the 2008 Mace Head EUCAARI intensive observing period: an overview , 2009 .

[23]  Paul A. Makar,et al.  Modelling the impacts of ammonia emissions reductions on North American air quality , 2009 .

[24]  Philippe Thunis,et al.  The impact of MM5 and WRF meteorology over complex terrain on CHIMERE model calculations , 2009 .

[25]  A. Russell,et al.  Quantifying the sources of ozone, fine particulate matter, and regional haze in the Southeastern United States. , 2009, Journal of environmental management.

[26]  Spyros N. Pandis,et al.  Evaluation of the volatility basis-set approach for the simulation of organic aerosol formation in the Mexico City metropolitan area , 2009 .

[27]  Philippe Thunis,et al.  The sensitivity of the CHIMERE model to emissions reduction scenarios on air quality in Northern Italy , 2009 .

[28]  S. Pandis,et al.  Simulating the formation of semivolatile primary and secondary organic aerosol in a regional chemical transport model. , 2009, Environmental science & technology.

[29]  Daniel J. Jacob,et al.  Effect of Climate Change on Air Quality , 2009 .

[30]  S. Pandis,et al.  Response of Fine Particulate Matter to Emission Changes of Oxides of Nitrogen and Anthropogenic Volatile Organic Compounds in the Eastern United States , 2008, Journal of the Air & Waste Management Association.

[31]  Spyros N. Pandis,et al.  Simulating secondary organic aerosol formation using the volatility basis-set approach in a chemical transport model , 2008 .

[32]  Allen L. Robinson,et al.  Effects of gas particle partitioning and aging of primary emissions on urban and regional organic aerosol concentrations , 2008 .

[33]  M. Sofiev,et al.  Impact of wild-land fires on European air quality in 2006–2008 , 2008 .

[34]  M. Sofiev,et al.  On integration of a Fire Assimilation System and a chemical transport model for near-real-time monitoring of the impact of wild-land fires on atmospheric composition and air quality. , 2008 .

[35]  Wenche Aas,et al.  Trends of nitrogen in air and precipitation: model results and observations at EMEP sites in Europe, 1980--2003. , 2008, Environmental pollution.

[36]  S. Pandis,et al.  Effect of NOx on secondary organic aerosol concentrations. , 2008, Environmental science & technology.

[37]  John P. Burrows,et al.  Satellite measurement based estimates of decadal changes in European nitrogen oxides emissions , 2008 .

[38]  Jean-Francois Lamarque,et al.  Predicted change in global secondary organic aerosol concentrations in response to future climate, emissions, and land use change , 2008 .

[39]  C. Stanier,et al.  Parameterization of secondary organic aerosol mass fractions from smog chamber data , 2008 .

[40]  Oriol Jorba,et al.  The use of a modelling system as a tool for air quality management: annual high-resolution simulations and evaluation. , 2008, The Science of the total environment.

[41]  E. M. Bailey,et al.  Response of atmospheric particulate matter to changes in precursor emissions: a comparison of three air quality models. , 2008, Environmental science & technology.

[42]  C. O'Dowd,et al.  A combined organic‐inorganic sea‐spray source function , 2008 .

[43]  Guillermo Rein,et al.  MODELLING, MONITORING AND MANAGEMENT OF FOREST FIRES , 2008 .

[44]  S. Pandis,et al.  Response of Inorganic Fine Particulate Matter to Emission Changes of Sulfur Dioxide and Ammonia: The Eastern United States as a Case Study , 2007, Journal of the Air & Waste Management Association.

[45]  G. Hidy,et al.  Effects of Sulfur Dioxide and Oxides of Nitrogen Emission Reductions on Fine Particulate Matter Mass Concentrations: Regional Comparisons , 2007, Journal of the Air & Waste Management Association.

[46]  R. Forkel,et al.  Nested regional climate-chemistry simulations for central Europe , 2007 .

[47]  F. Giorgi,et al.  Modelling the regional effects of climate change on air quality , 2007 .

[48]  Qi Zhang,et al.  Ubiquity and dominance of oxygenated species in organic aerosols in anthropogenically‐influenced Northern Hemisphere midlatitudes , 2007 .

[49]  Allen L Robinson,et al.  Rethinking Organic Aerosols: Semivolatile Emissions and Photochemical Aging , 2007, Science.

[50]  Philippe Thunis,et al.  Evaluation of long-term ozone simulations from seven regional air quality models and their ensemble , 2007 .

[51]  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.

[52]  Steven J. Smith,et al.  Sulphate trends in Europe: are we able to model the recent observed decrease , 2007 .

[53]  Philippe Thunis,et al.  Analysis of model responses to emission-reduction scenarios within the CityDelta project , 2007 .

[54]  Frédérik Meleux,et al.  Increase in summer European ozone amounts due to climate change , 2006 .

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

[56]  J. Ortega,et al.  Sesquiterpene emissions from loblolly pine and their potential contribution to biogenic aerosol formation in the Southeastern US , 2006 .

[57]  Laurence Rouil,et al.  Are decadal anthropogenic emission reductions in Europe consistent with surface ozone observations? , 2006 .

[58]  R. Vautard,et al.  Future global tropospheric ozone changes and impact on European air quality , 2006 .

[59]  Renate Forkel,et al.  Regional climate change and its impact on photooxidant concentrations in southern Germany: Simulations with a coupled regional climate‐chemistry model , 2006 .

[60]  A L Robinson,et al.  Coupled partitioning, dilution, and chemical aging of semivolatile organics. , 2006, Environmental science & technology.

[61]  M. Kleeman,et al.  Control strategies for the reduction of airborne particulate nitrate in California's San Joaquin Valley , 2005 .

[62]  Hilde Fagerli,et al.  Can we explain the trends in European ozone levels , 2005 .

[63]  Jordan G. Powers,et al.  A Description of the Advanced Research WRF Version 2 , 2005 .

[64]  Joakim Langner,et al.  Impact of climate change on surface ozone and deposition of sulphur and nitrogen in Europe , 2005 .

[65]  Johannes Staehelin,et al.  Changes of daily surface ozone maxima in Switzerland in all seasons from 1992 to 2002 and discussion of summer 2003 , 2004 .

[66]  E. M. Bailey,et al.  Geographic sensitivity of fine particle mass to emissions of SO2 and NOx. , 2004, Environmental science & technology.

[67]  Bonyoung Koo,et al.  Integrated approaches to modeling the organic and inorganic atmospheric aerosol components , 2003 .

[68]  R. Vautard,et al.  O3‐NOx‐VOC sensitivity and NOx‐VOC indicators in Paris: Results from models and Atmospheric Pollution Over the Paris Area (ESQUIF) measurements , 2003 .

[69]  S. Pandis,et al.  Development and application of an efficient moving sectional approach for the solution of the atmospheric aerosol condensation/evaporation equations , 2003 .

[70]  M. Sutton,et al.  The European perspective on nitrogen emission and deposition. , 2003, Environment international.

[71]  Mark A. Sutton,et al.  Establishing the Link between Ammonia Emission Control and Measurements of Reduced Nitrogen Concentrations and Deposition , 2003, Environmental monitoring and assessment.

[72]  A. Stein,et al.  Chemical indicators of sulfate sensitivity to nitrogen oxides and volatile organic compounds , 2002 .

[73]  J. Lelieveld,et al.  Global Air Pollution Crossroads over the Mediterranean , 2002, Science.

[74]  C. Moulin,et al.  Aerosol sources and their contribution to the chemical composition of aerosols in the Eastern Mediterranean Sea during summertime , 2002 .

[75]  D. Dabdub,et al.  NO x and VOC Control and Its Effects on the Formation of Aerosols , 2002 .

[76]  Spyros N. Pandis,et al.  Optimizing model performance: variable size resolution in cloud chemistry modeling , 2001 .

[77]  C. Seigneur,et al.  Sensitivity of particulate matter nitrate formation to precursor emissions in the California San Joaquin Valley. , 2001, Environmental science & technology.

[78]  Charles L. Blanchard,et al.  Ozone response to precursor controls: comparison of data analysis methods with the predictions of photochemical air quality simulation models , 2001 .

[79]  Jostein K. Sundet,et al.  Model calculations of present and future levels of ozone and ozone precursors with a global and a regional model , 2001 .

[80]  A. Nenes,et al.  MADM-A New Multicomponent Aerosol Dynamics Model , 2000 .

[81]  S. Pandis,et al.  A computationally efficient hybrid approach for dynamic gas/aerosol transfer in air quality models , 2000 .

[82]  A. Stein,et al.  The sensitivity of sulfur wet deposition to atmospheric oxidants , 2000 .

[83]  H. Bingemer,et al.  Biogenic sulphate generation in the Mediterranean Sea and its contribution to the sulphate anomaly in the aerosol over Israel and the Eastern Mediterranean , 2000 .

[84]  R. Monson,et al.  Modelling changes in VOC emission in response to climate change in the continental United States , 1999 .

[85]  Sandra L. Winkler,et al.  The impact of an 8 h ozone air quality standard on ROG and NOx controls in Southern California , 1999 .

[86]  G. Tonnesen Effects of uncertainty in the reaction of the hydroxyl radical with nitrogen dioxide on model-simulated ozone control strategies , 1999 .

[87]  Alan Krupnick,et al.  Costs and Benefits of Reducing Air Pollutants Related to Acid Rain , 1998 .

[88]  Spyros N. Pandis,et al.  Response of Inorganic PM to Precursor Concentrations , 1998 .

[89]  A. Nenes,et al.  ISORROPIA: A New Thermodynamic Equilibrium Model for Multiphase Multicomponent Inorganic Aerosols , 1998 .

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

[91]  Donald Dabdub,et al.  Chemical Coupling Between Atmospheric Ozone and Particulate Matter , 1997 .

[92]  P. Bousquet,et al.  Tropospheric aerosol ionic composition in the Eastern Mediterranean region , 1997 .

[93]  Donald L. Singleton,et al.  Sensitivity of ozone concentrations to VOC and NOx emissions in the Canadian Lower Fraser Valley , 1997 .

[94]  D. Simpson,et al.  Biogenic emissions in Europe: 2. Implications for ozone control strategies , 1995 .

[95]  J. Seinfeld,et al.  Secondary organic aerosol formation and transport — II. Predicting the ambient secondary organic aerosol size distribution☆ , 1993 .

[96]  J. Seinfeld,et al.  Secondary organic aerosol formation and transport , 1992 .

[97]  J. Seinfeld,et al.  Sensitivity analysis of a chemical mechanism for aqueous‐phase atmospheric chemistry , 1989 .

[98]  M. Wesely Parameterization of surface resistances to gaseous dry deposition in regional-scale numerical models , 1989 .

[99]  Armistead G. Russell,et al.  Verification of a mathematical model for aerosol nitrate and nitric acid formation and its use for control measure evaluation , 1986 .

[100]  W. Stockwell,et al.  The mechanism of the HO-SO2 reaction , 1983 .

[101]  J. Seinfeld,et al.  Thermodynamic prediction of the water activity, NH4NO3 dissociation constant, density and refractive index for the NH4NO3-(NH4)2SO4-H2O system at 25°C , 1982 .

[102]  G. Sehmel Particle and gas dry deposition: A review , 1980 .

[103]  W. Slinn,et al.  Predictions for particle deposition on natural waters , 1980 .