Temporal trends in the isotope signature of air-borne sulfur in Central Europe

被引:68
作者
Novák, M [1 ]
Jacková, I [1 ]
Prechová, E [1 ]
机构
[1] Czech Geol Survey, Prague 15200 5, Czech Republic
关键词
D O I
10.1021/es0000753
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
In various parts of the Northern hemisphere air-borne S exhibits a seasonality, with isotopically light (i.e., 32S-rich) sulfur predominating in the warm summer months. Such seasonality has been reported from the United States, Ca nad a, Japan, and China. Elevated biological emissions of isotopically light S in summer, a temperature-dependent isotope fractionation accompanying the oxidation of SO2, and heavy rains in winter bringing S-34-rich marine S have been suggested:as the controlling mechanisms. In the atmosphere of Central Europe, one of the most severely polluted regions of the world, we have found an opposite seasonal trend: Isotopically light SO2-S predominates in the cold winter months, whereas isotopically heavy SO2-S is typical of the summer; The low delta S-34 values of airborne SO2 in winter are influenced by low-delta S-34 emissions from local coal-burning power plants. The coal contains isotopically light S (mean delta S-34 0f 1.6 parts per thousand). Higher demand for electricity during the heating season leads-to higher anthropogenic S emission rates in:winter. On a yearly basis, atmospheric sulfate S in Central Europe is isotopically heavier than atmospheric SO2-S by 4 parts per thousand. Atmospheric oxidation of SO2 is accompanied by an isotope fractionation resulting in S-34-enriched sulfate. In addition to the seasonality in air-borne delta S-34(SO2) we report also an interannual trend of 1 parts per thousand yr(-1) toward isotopically light sulfate S in atmospheric deposition. This interannual trend cannot be explained by a change in pollution sources accompanying the present massive environmental cleanup. To investigate the role of biological S emissions from; the soil of heavily polluted ecosystems, we conducted a series of laboratory experiments using repacked soil columns and 34S-enriched precipitation under summer and winter temperatures. These experiments indicate that, under summer temperatures, the S-34-labeled precipitation is largely captured by the upper organic-rich soil horizons, a high proportion (53-74%) of S input is revolatilized, and the biologically reemitted S is isotopically light. Under winter temperatures more precipitation S is leached to the bottom of the soil columns. Our experiments have shown that biological emissions in Central Europe can be sizable. Yet, they cannot be singled out in the overall SO2 isotope pattern in the atmosphere. The main reason is continuous, variable (0-4 parts per thousand), open-system depletion in S-34 in the residual SO2 during the isotopically selective SO2-to-SO(4)(2-)conversion.
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页码:255 / 260
页数:6
相关论文
共 36 条
[1]   Patterns of stable S isotopes in a forested catchment as indicators for biological S turnover [J].
Alewell, C ;
Gehre, M .
BIOGEOCHEMISTRY, 1999, 47 (03) :319-333
[2]   Assessing the origin of sulfate deposition at the Hubbard Brook Experimental Forest [J].
Alewell, C ;
Mitchell, MJ ;
Likens, GE ;
Krouse, R .
JOURNAL OF ENVIRONMENTAL QUALITY, 2000, 29 (03) :759-767
[3]  
ANGLE JS, 2000, HDB SOIL SCI
[4]   ESTIMATES OF RESIDENCE TIMES OF SULFATE AEROSOLS IN AMBIENT AIR [J].
BONDIETTI, EA ;
PAPASTEFANOU, C .
SCIENCE OF THE TOTAL ENVIRONMENT, 1993, 136 (1-2) :25-31
[5]  
Caron F., 1986, APPL GEOCHEM, V1, P601
[6]   Recovery of surface waters in the northeastern US, from decreases in atmospheric deposition of sulfur [J].
Driscoll, CT ;
Likens, GE ;
Church, MR .
WATER AIR AND SOIL POLLUTION, 1998, 105 (1-2) :319-329
[7]  
Egiazarov A. C., 1971, ISOTOPENPRAXIS, V7, P379
[8]   SULFUR ISOTOPE-EFFECTS .1. ISOTOPIC-EXCHANGE COEFFICIENT FOR SULFUR ISOTOPES S-34-S-32 IN SYSTEM SO2G-HSO3-AQ AT 25, 35, AND 45 DEGREES C [J].
ERIKSEN, TE .
ACTA CHEMICA SCANDINAVICA, 1972, 26 (02) :573-&
[9]   Changes in mass element fluxes and their importance for critical loads: GEOMON network, Czech Republic [J].
Fottova, D ;
Skorepova, I .
WATER AIR AND SOIL POLLUTION, 1998, 105 (1-2) :365-376
[10]   Biogeochemistry of iron and sulfur in sediments of an acidic mining lake in Lusatia, Germany [J].
Friese, K ;
Wendt-Potthoff, K ;
Zachmann, DW ;
Fauville, A ;
Mayer, B ;
Veizer, J .
WATER AIR AND SOIL POLLUTION, 1998, 108 (3-4) :231-247