MAGIC, SAFE and SMART model applications at integrated monitoring sites: Effects of emission reduction scenarios

被引:26
作者
Forsius, M
Alveteg, M
Jenkins, A
Johansson, M
Kleemola, S
Lukewille, A
Posch, M
Sverdrup, H
Walse, C
机构
[1] Finnish Environm Inst, FIN-00251 Helsinki, Finland
[2] Univ Lund, Dept Chem Engn 2, S-22100 Lund, Sweden
[3] Inst Hydrol, Wallingford OX10 8BB, Oxon, England
[4] Norwegian Inst Air Res, N-2007 Kjeller, Norway
[5] RIVM, NL-3720 BA Bilthoven, Netherlands
关键词
acidification; emission; MAGIC; model; nitrogen; SAFE; SMART; sulfur;
D O I
10.1023/A:1005099930089
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Three well-known dynamic acidification models (MAGIC, SAFE, SMART) were applied to data sets from five Integrated Monitoring sites in Europe. The calibrated models were used in a policy-oriented framework to predict the long-term soil acidification of these background forest sites, given different scenarios of future deposition of S and N. Emphasis was put on deriving realistic site-specific scenarios for the model applications. The deposition was calculated with EMEP transfer matrices and official emissions for the target years 2000, 2005 and 2010. The alternatives for S deposition were current reduction plans and maximum feasible reductions. For N, the NOx and NHy depositions were frozen at the present level. For NOx, a reduction scenario of flat 30 % reduction from present deposition also was utilized to demonstrate the possible effects of such a measure. The three models yielded generally consistent results. The 'Best prediction'-scenario (including the effects of the second UN/ECE protocol for reductions of SO2 emissions and present level for NOx-emissions), resulted in many cases in a stabilization of soil acidification, although significant improvements were not always shown. With the exception of one site, the 'Maximum Feasible Reductions' scenario always resulted in significant improvements. Dynamic models are needed as a complement to steady-state techniques for estimating critical loads and assessing emission reduction policies, where adequate data are available.
引用
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页码:21 / 30
页数:10
相关论文
共 23 条
[1]  
ALVETEG M, 1998, UNPUB WAT AIR SOIL P
[2]   MODELED HISTORICAL CONCENTRATIONS AND DEPOSITIONS OF AMMONIA AND AMMONIUM IN EUROPE [J].
ASMAN, WAH ;
DRUKKER, B ;
JANSSEN, AJ .
ATMOSPHERIC ENVIRONMENT, 1988, 22 (04) :725-735
[3]   Critical loads - Possibilities and constraints [J].
Bull, KR .
WATER AIR AND SOIL POLLUTION, 1995, 85 (01) :201-212
[4]  
COFALA J, 1995, 15 M UNECE TASK FORC
[5]   MODELING THE EFFECTS OF ACID DEPOSITION - ASSESSMENT OF A LUMPED PARAMETER MODEL OF SOIL-WATER AND STREAMWATER CHEMISTRY [J].
COSBY, BJ ;
HORNBERGER, GM ;
GALLOWAY, JN ;
WRIGHT, RF .
WATER RESOURCES RESEARCH, 1985, 21 (01) :51-63
[6]   MODELING CRITICAL LOADS FOR THE SOLLING SPRUCE SITE [J].
DEVRIES, W ;
POSCH, M ;
OJA, T ;
VANOENE, H ;
KROS, H ;
WARFVINGE, P ;
ARP, PA .
ECOLOGICAL MODELLING, 1995, 83 (1-2) :283-293
[7]   SIMULATION OF SOIL RESPONSE TO ACIDIC DEPOSITION SCENARIOS IN EUROPE [J].
DEVRIES, W ;
REINDS, GJ ;
POSCH, M ;
KAMARI, J .
WATER AIR AND SOIL POLLUTION, 1994, 78 (3-4) :215-246
[8]   SIMULATION OF THE LONG-TERM SOIL RESPONSE TO ACID DEPOSITION IN VARIOUS BUFFER RANGES [J].
DEVRIES, W ;
POSCH, M ;
KAMARI, J .
WATER AIR AND SOIL POLLUTION, 1989, 48 (3-4) :349-390
[9]  
Forsius Martin, 1997, Boreal Environment Research, V2, P129
[10]  
HEDIN LO, 1994, NATURE, V367, P351, DOI 10.1038/367351a0