Recovery from acidification in central Europe -: observed and predicted changes of soil and streamwater chemistry in the Lysina. catchment, Czech Republic

被引:76
作者
Hruska, J
Moldan, F
Krám, P
机构
[1] Czech Geol Survey, Prague 11821 1, Czech Republic
[2] IVL Swedish Environm Res Inst, SE-40258 Gothenburg, Sweden
[3] Swedish Univ Agr Sci, Dept Environm Assessment, SE-75007 Uppsala, Sweden
关键词
MAGIC model; small catchment; soil and water acidification; Czech Republic;
D O I
10.1016/S0269-7491(02)00149-5
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The geochemical model MAGIC was applied to estimate streamwater and soil chemistry between 1851 and 2030 at the Lysina catchment, an acid-sensitive granitic catchment covered by planted Norway spruce monoculture in the western Czech Republic, The total deposition of sulfur to the catclurient was 164 rneq M-2 in 1991, but had declined to 52 meq M-2 by 2000. Although S02 emissions in the region declined by 90% compared to the 1980s, acidification recovery was small within the period 1990-2000. Stream pH increased only slightly (from 3.92 to 4.07), although SO(4) concentration declined sharply from 568 mueq l(-1) (1990) to 232 mueq l(-1) (2000). Organic acids played an important role in streamwater buffering. According to the MAGIC prediction using deposition measured in 1999 2000, streamwater pH will increase to 4.3 and soil base saturation will increase to 6.2% by 2030 (from 5.7% in 2002). Pre-industrial pH was estimated to be 5.5 and soil base saturation 24.7%. The loss of base cations (Ca, Mg, Na, K) was caused predominantly by atmospheric acidity, but intensive forestry was responsible for approximately one third of the net base cation loss via accumulation in harvested biomass. Severely damaged sites, under continued pressure from forestry, will not return to a good environmental status in the near future (if ever) when the acid deposition input is only partially reduced. (C) 2002 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:261 / 274
页数:14
相关论文
共 42 条
[1]   Use of objective criteria for the assessment of biogeochemical ecosystem models [J].
Alewell, C ;
Manderscheid, B .
ECOLOGICAL MODELLING, 1998, 107 (2-3) :213-224
[2]   Describing soil SO42- dynamics in the Solling roof project with 4 two different modelling approaches [J].
Alewell, C ;
Manderscheid, B ;
Lukewille, A ;
Koeppe, P ;
Prenzel, J .
WATER AIR AND SOIL POLLUTION, 1995, 85 (03) :1801-1806
[3]  
BREDEMEIER M, 1988, WATER AIR SOIL POLL, V40, P121
[4]   MODELING THE EFFECTS OF ACID DEPOSITION - ESTIMATION OF LONG-TERM WATER-QUALITY RESPONSES IN A SMALL FORESTED CATCHMENT [J].
COSBY, BJ ;
WRIGHT, RF ;
HORNBERGER, GM ;
GALLOWAY, JN .
WATER RESOURCES RESEARCH, 1985, 21 (11) :1591-1601
[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]  
COSBY BJ, 1991, MAGIC MODEL ACIDIFIC
[7]   Synthesis of nitrogen pools and fluxes from European forest ecosystems [J].
Dise, NB ;
Matzner, E ;
Gundersen, P .
WATER AIR AND SOIL POLLUTION, 1998, 105 (1-2) :143-154
[8]   MAGIC, SAFE and SMART model applications at integrated monitoring sites: Effects of emission reduction scenarios [J].
Forsius, M ;
Alveteg, M ;
Jenkins, A ;
Johansson, M ;
Kleemola, S ;
Lukewille, A ;
Posch, M ;
Sverdrup, H ;
Walse, C .
WATER AIR AND SOIL POLLUTION, 1998, 105 (1-2) :21-30
[9]   Nitrate leaching in forest ecosystems is related to forest floor C/N ratios [J].
Gundersen, P ;
Callesen, I ;
de Vries, W .
ENVIRONMENTAL POLLUTION, 1998, 102 :403-407
[10]  
HANAMAN J, 1896, DISSOLVED CHARACTERI, V1