Deposition and emissions of reactive nitrogen over European forests: A modelling study

被引:62
作者
Simpson, D. [1 ]
Butterbach-Bahl, K.
Fagerli, H.
Kesik, M.
Skiba, U.
Tang, S.
机构
[1] Norwegian Meteorol Inst, Oslo, Norway
[2] Forschungszentrum Karlsruhe, Inst Meteorol & Climate Res, Garmisch Partenkirchen, Germany
[3] Ctr Ecol & Hydrol, Penicuik, Midlothian, Scotland
[4] Chalmers Tech Univ, Dept Radio & Space Sci, Gothenburg, Sweden
基金
英国自然环境研究理事会;
关键词
nitrogen oxides; deposition; soil emissions; modelling; EMEP;
D O I
10.1016/j.atmosenv.2006.04.063
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The EMEP MSC-W Eulerian chemical transport model is used to investigate a number of features concerning the concentrations and depositions of reactive nitrogen species over Europe, with a focus on forest ecosystems and soil emissions. We illustrate the relative contributions of oxidised versus reduced nitrogen, and of dry versus wet deposition, to nitrogen inputs to forests. A comparison with measurements, including data for the NOFRETETE sites, showed that the EMEP model performs generally well for N-compounds, although with some problems for NH3 which is difficult to model with a large-scale model. The model was modified to make use of a new forest-soil-NO inventory (with daily resolution) from the NOFRETETE project and used to calculate the potential effects of these emissions on N-deposition to forests, and on the ozone-indicator AOT40. The contribution of soil-NO to these environmental measures was found to be generally small, but significant in some areas, with changes ranging between 0-20% in Central Europe and even greater in Scandinavia. Given the large uncertainties in soil-NO emission estimates, it is clear that this source is potentially comparable in its importance to many combustion sources in parts of Europe, and deserves more attention. (c) 2006 Elsevier Ltd. All rights reserved.
引用
收藏
页码:5712 / 5726
页数:15
相关论文
共 73 条
[1]  
AAS W, 2004, 42004 ENEP NILU
[2]  
[Anonymous], 2003, 12003 EMEP NORW MET
[3]   EMISSION OF NITRIC-OXIDE (NO) FROM TROPICAL FOREST SOILS AND EXCHANGE OF NO BETWEEN THE FOREST CANOPY AND ATMOSPHERIC BOUNDARY-LAYERS [J].
BAKWIN, PS ;
WOFSY, SC ;
FAN, SM ;
KELLER, M ;
TRUMBORE, SE ;
DACOSTA, JM .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 1990, 95 (D10) :16755-16764
[4]   A regional scale multi-layer model for the calculation of long-term transport and deposition of air pollution in Europe [J].
Berge, E ;
Jakobsen, HA .
TELLUS SERIES B-CHEMICAL AND PHYSICAL METEOROLOGY, 1998, 50 (03) :205-223
[5]   Validation of nitrogen dioxide diffusion tube methodology in the UK [J].
Bush, T ;
Smith, S ;
Stevenson, K ;
Moorcroft, S .
ATMOSPHERIC ENVIRONMENT, 2001, 35 (02) :289-296
[6]   Fluxes of NO and N2O from temperate forest soils: impact of forest type, N deposition and of liming on the NO and N2O emissions [J].
ButterbachBahl, K ;
Gasche, R ;
Breuer, L ;
Papen, H .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1997, 48 (1-2) :79-90
[7]   Concentrations of ammonia and nitrogen dioxide at roadside verges, and their contribution to nitrogen deposition [J].
Cape, JN ;
Tang, YS ;
van Dijk, N ;
Love, L ;
Sutton, MA ;
Palmer, SCF .
ENVIRONMENTAL POLLUTION, 2004, 132 (03) :469-478
[8]   A global inventory of nitric oxide emissions from soils [J].
Davidson, EA ;
Kingerlee, W .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1997, 48 (1-2) :37-50
[9]  
Davidson EA, 1998, ECOL APPL, V8, P748, DOI 10.1890/1051-0761(1998)008[0748:MEORNO]2.0.CO
[10]  
2