Implementation and evaluation of pH-dependent cloud chemistry and wet deposition in the chemical transport model REM-Calgrid

The Chemistry Transport Model REM-Calgrid (RCG) has been improved by implementing an enhanced description of aqueous-phase chemistry and wet deposition processes including droplet pH. A sensitivity study on cloud and rain droplet pH has been performed to investigate its impact on model sulphate production and gas wet scavenging. Air concentrations and wet deposition fluxes of the model sensitivity runs have been analysed and compared to observations. It was found that droplet pH variation within atmospheric ranges affects modelled air concentrations and wet deposition fluxes significantly. Applying a droplet pH of 5.5 for July 2005, mean sulphate air concentrations increased by up to 10% compared to using a droplet pH of 5 while SO 2 domain wet deposition sum increased by 110%. Moreover, model results using modelled droplet pH for January and July 2005 have been compared to model results applying a constant pH of 5 and to observations. The comparison to observations has shown that using a variable droplet pH improves the model performance concerning air concentrations and wet deposition fluxes of the investigated sulphur and nitrogen compounds. For SO x wet deposition fluxes the Root Mean Square Error (RMSE) decreased by 16% for July 2005 when using a variable droplet pH instead of a constant pH of 5. Concerning sulphate and SO 2 air concentrations the RMSE was reduced by 8% and 16% for July 2005, respectively. The results have revealed that applying a variable droplet pH is preferable to using a constant pH leading to better consistency concerning air concentrations and wet deposition fluxes. © 2011 Elsevier Ltd.

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

[2]  M. A. Sutton,et al.  Plant—atmosphere exchange of ammonia , 1995, Philosophical Transactions of the Royal Society of London. Series A: Physical and Engineering Sciences.

[3]  K. Roy,et al.  Analysis of cloud and precipitation chemistry at Whiteface Mountain, NY , 2009 .

[4]  D. Byun Science algorithms of the EPA Models-3 community multi-scale air quality (CMAQ) modeling system , 1999 .

[5]  R. Vautard,et al.  Aerosol modeling with CHIMERE—preliminary evaluation at the continental scale , 2004 .

[6]  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.

[7]  L. Alados-Arboledas,et al.  Chemical composition of wet precipitation at the background EMEP station in Víznar (Granada, Spain) (2002–2006) , 2010 .

[8]  F. Anselmet,et al.  Aerosol dry deposition on vegetative canopies. Part I: Review of present knowledge , 2008 .

[9]  I. Ilyin,et al.  Co-operative Programme for Monitoring and Evaluation of the Long-Range Transmission of Air Pollutants in Europe EMEP , 2001 .

[10]  Jan G. M. Roelofs,et al.  The effects of air‐borne nitrogen pollutants on species diversity in natural and semi‐natural European vegetation , 1998 .

[11]  P. Kraft,et al.  Critical loads and their exceedances at intensive forest monitoring sites in Europe. , 2008, Environmental pollution.

[12]  M. Stähli,et al.  An Overview of Atmospheric Deposition Chemistry over the Alps: Present Status and Long-term Trends , 2006, Hydrobiologia.

[13]  J. Lamarque,et al.  Nitrogen and sulfur deposition on regional and global scales: A multimodel evaluation , 2006 .

[14]  Graeme L. Stephens,et al.  Remote Sensing of the Lower Atmosphere: An Introduction , 1994 .

[15]  R. Derwent,et al.  Sensitivity of modelled sulphate and nitrate aerosol to cloud, pH and ammonia emissions , 2009 .

[16]  D. Byun,et al.  Review of the Governing Equations, Computational Algorithms, and Other Components of the Models-3 Community Multiscale Air Quality (CMAQ) Modeling System , 2006 .

[17]  Erik Berge,et al.  A regional scale multilayer model for the calculation of long‐term transport and deposition of air pollution in Europe , 1998 .

[18]  Alma Hodzic,et al.  A model inter-comparison study focussing on episodes with elevated PM10 concentrations , 2008 .

[19]  P. Nowacki,et al.  CAPRAM2.3: A Chemical Aqueous Phase Radical Mechanism for Tropospheric Chemistry , 2000 .

[20]  A. Venkatram,et al.  The contribution of in-cloud oxidation of SO2 to wet scavenging of sulfur in convective clouds , 1985 .

[21]  H. Puxbaum,et al.  A study of the influence of riming of ice crystals on snow chemistry during different seasons in precipitating continental clouds , 1994 .

[22]  M. Beekmann,et al.  PM measurement campaign HOVERT in the Greater Berlin area: model evaluation with chemically specified particulate matter observations for a one year period , 2006 .

[23]  L. Poulain,et al.  Towards a more detailed description of tropospheric aqueous phase organic chemistry: CAPRAM 3.0 , 2005 .

[24]  C. Walcek Minor flux adjustment near mixing ratio extremes for simplified yet highly accurate monotonic calculation of tracer advection , 2000 .

[25]  J. Staehelin,et al.  Cloud chemistry at Mt Rigi, Switzerland: Dependence on drop size and relationship to precipitation chemistry , 1993 .

[26]  R. Wolke,et al.  Towards an operational aqueous phase chemistry mechanism for regional chemistry-transport models: CAPRAM-RED and its application to the COSMO-MUSCAT model , 2009 .

[27]  A. Nenes,et al.  Continued development and testing of a new thermodynamic aerosol module for urban and regional air quality models , 1999 .

[28]  R. Rogers,et al.  A short course in cloud physics , 1976 .

[29]  Renske Timmermans,et al.  The LOTOS?EUROS model: description, validation and latest developments , 2008 .

[30]  E. Reimer,et al.  An Operational Meteorological Diagnostic System for Regional Air Pollution Analysis and Long Term Modeling , 1992 .

[31]  Leiming Zhang,et al.  A size-segregated particle dry deposition scheme for an atmospheric aerosol module , 2001 .

[32]  Robert Yamartino,et al.  Chapter 4.12 Analyzing the response of a chemical transport model to emissions reductions utilizing various grid resolutions , 2006 .

[33]  A. Berner,et al.  Cloudwater chemistry in the subcooled droplet regime at Mount Sonnblick (3106 M A.S.L., Salzburg, Austria) , 1994, Water, Air, and Soil Pollution.

[34]  M. Hoffmann,et al.  Kinetics and mechanism of the oxidation of aquated sulfur dioxide by hydrogen peroxide at low pH , 1983 .

[35]  J. Erisman,et al.  Parametrization of surface resistance for the quantification of atmospheric deposition of acidifying pollutants and ozone , 1994 .

[36]  R. Wright,et al.  Impact of acid precipitation on freshwater ecosystems in Norway , 1976 .

[37]  Philippe Thunis,et al.  Skill and uncertainty of a regional air quality model ensemble , 2009 .

[38]  Philippe Thunis,et al.  Evaluation and intercomparison of Ozone and PM10 simulations by several chemistry transport models over four European cities within the CityDelta project , 2007 .

[39]  B. Albrecht,et al.  Surface‐based remote sensing of the observed and the Adiabatic liquid water content of stratocumulus clouds , 1990 .

[40]  Spyros N. Pandis,et al.  Size‐resolved aqueous‐phase atmospheric chemistry in a three‐dimensional chemical transport model , 2003 .

[41]  S. Solberg,et al.  Time series study of concentrations of SO4(2-) and H+ in precipitation and soil waters in Norway. , 2002, Environmental pollution.

[42]  D. Fowler,et al.  Changes in the atmospheric deposition of acidifying compounds in the UK between 1986 and 2001. , 2005, Environmental pollution.

[43]  R. Barthelmie,et al.  A review of measurement and modelling results of particle atmosphere–surface exchange , 2008 .