MOVEMENT AND TRANSFORMATION OF S-35 LABELED SULFATE IN THE SOIL OF A HEAVILY POLLUTED SITE IN THE NORTHERN CZECH-REPUBLIC

被引:10
作者
NOVAK, M
PRECHOVA, E
机构
[1] Czech Geological Survey, Prague 5, 152 00
关键词
SOIL SULFUR; S-35; RADIOLABELING; SOIL INCUBATION;
D O I
10.1007/BF00146710
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Changes in chemistry and vertical distribution of S-35 were investigated in column experiments using intact topsoil and repacked mineral soil horizons 1 to 20 weeks after tracer application (901 kBq S-35-SO42- per column 6.5 cm in diameter). Horizons O, A, AE and Bvs of an Orthic Podzol were incubated at 20 degrees C and wetted twice a week with 1 1 mm of natural throughfall precipitation (38.5 mg SO42- L(-1), pH 3.3). The top 35 cm of the soil contained 1,290 kg S ha(-1), or 18 times more than is the annual atmospheric S input (71.4 kg S ha(-1) yr(-1)). Of this amount, 17.8 % was stored as inorganic sulphate S, 4.6 % as reduced inorganic S, and 77.6 % as organic S. In O+A and AE, free sulphate was the most abundant S-35 form, while in Bvs the S-35 activity of free and adsorbed sulphate was similar. The proportion of adsorbed sulphate increased with depth, averaging 23, 30 and 47 % of total inorganic sulphate S-35 in O+A, AE and Bvs, respectively. Total specific activity of chemically transformed S-35 (i.e., of reduced inorganic S and organic S) constituted 3.4, 3.8 and 105 % of inorganic sulphate S-35 activity in O+A, AE and Bvs, respectively, in averaged weeks 2-4, and 7.5, 6.4 and 39.6 % in averaged weeks 11-13 in O+A, AE and Bvs, respectively. The turnover time of C-bonded S-35 was Shorter than that of ester sulphate S-35. A, increase in FeS2-S-35 with time indicated anaerobic conditions suitable for bacterial sulphate reduction. After 13 weeks, 68 % of the tracer was found deeper than 8 cm below soil surface.
引用
收藏
页码:83 / 94
页数:12
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共 32 条
[11]  
Harrison R.B., Johnson D.W., Todd D.E., Sulfate adsorption and desorption reversibility in a variety of forest soils, Journal of Environmental Quality, 18, pp. 419-426, (1989)
[12]  
Hillel D., Fundamentals of Soil Physics, (1980)
[13]  
Houle D., Carignan R., Sulfur speciation and distribution in soils and aboveground biomass of a boreal coniferous forest, Biogeochemistry, 16, pp. 63-82, (1992)
[14]  
Johnson D.W., Henderson G.S., Huff D.D., Lindberg S.E., Richter D.D., Shriner D.S., Todd D.E., Turner J., Cycling of organic and inorganic sulphur in a chestnut oak forest, Oecologia, 54, pp. 141-148, (1982)
[15]  
Johnson D.W., Lindberg S.E., Atmospheric deposition and the forest nutrient cycling, (1992)
[16]  
Likens G.E., Bormann F.H., Pierce R.S., Eaton J.S., Johnson N.M., Biogeochemistry of a Forested Ecosystem, (1977)
[17]  
Mitchell M.J., Fuller R.D., Models of sulfur dynamics in forest and grassland ecosystems with emphasis on soil processes, Biogeochemistry, 5, pp. 133-163, (1988)
[18]  
Mitchell M.J., David M.B., Harrison R.B., Sulphur dynamics of forest ecosystems, Sulphur cycling on the continents, (1992)
[19]  
Moldan B., Environment of the Czech Republic. Development and State at the End of 1989, (1990)
[20]  
Moldan B., Biogeochemistry of small catchments, (1994)