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
相关论文
共 32 条
[1]  
Autry A.R., Fitzgerald J.W., Application of the heterotrophic activity method to organosulfur formation in forest soils, Soil Biology and Biochemistry, 22, pp. 743-748, (1990)
[2]  
Bolan N.S., Scotter D.R., Syers J.K., Tillman R.W., The effect of adsorption on sulfate leaching, Soil Science Society of America Journal, 50, pp. 1419-1424, (1986)
[3]  
Canfield D.E., Raiswell R., Westrich J.T., Reaves, Berner R.A., The use of chromium reduction in the analysis of reduced inorganic sulfur in sediments and shales, Chemical Geology, 54, pp. 149-155, (1986)
[4]  
Cape J.N., The use of<sup>35</sup>S to study sulphur cycling in forests, Environmental Geochemistry and Health, 15, pp. 113-118, (1993)
[5]  
David M.B., Mitchell M.J., Scott T.J., Importance of biological processes in the sulfur budget of a northern hardwood ecosystem, Biological Fertility of Soils, 5, pp. 258-264, (1987)
[6]  
Dhamala B.R., Mitchell M.J., Stam A.C., Sulfur dynamics in mineral horizons of two northern hardwood soils. A column study with<sup>35</sup>S, Biogeochemistry, 10, pp. 143-160, (1990)
[7]  
Fitzgerald J.W., Ash J.T., Strickland T.C., Swank W.T., Formation of organic sulfur in forest soils: A biologically mediated process, Canadian Journal of Forestry Research, 13, pp. 1077-1082, (1983)
[8]  
Foth H.D., Fundamentals of Soil Science, (1984)
[9]  
Freney J.R., Some observations on the nature of organic sulphur compounds in soil, Australian Journal of Agricultural Research, 12, pp. 424-432, (1961)
[10]  
Fuller R.D., Mitchell M.J., Krouse H.R., Wyskowski B.J., Driscoll C.T., Stable sulfur isotope ratios as a tool for interpreting ecosystem sulfur dynamics, Water, Air and Soil Pollution, 28, pp. 163-171, (1986)