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Published online 25 January 2007
Published in J Environ Qual 36:379-385 (2007)
DOI: 10.2134/jeq2006.0374
© 2007 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Effect of Dissolved Organic Carbon on Zinc Solubility in Incubated Biosolids-Amended Soils

Vasileios Antoniadisa,*, Christos D. Tsadilasb and Stamatis Stamatiadisc

a Dep. of Agricultural Development, Democritus Univ. of Thrace, 193 Pantazidou St., GR-682 00, Orestiada, Greece
b National Agricultural Research Foundation, Institute of Soil Mapping and Classification, 1 Theofrastos St., Larissa, GR-413 35, Greece
c Soil Ecology and Biotechnology Lab., Goulandris Natural History Museum, GAIA Center, 13 Levidou St., GR-145 62, Kifissia, Greece


Figure 1
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  		Fig. 1. pH values during incubation of unamended and biosolids-amended soils. Error bars indicate standard deviation (n = 3).

 

Figure 2
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  		Fig. 2. Soil organic C dynamics during incubation of unamended and biosolids-amended soils. Error bars indicate standard deviation (n = 3).

 

Figure 3
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  		Fig. 3. Dissolved organic C dynamics during incubation of unamended and biosolids-amended soils. Error bars indicate standard deviation (n = 3).

 

Figure 4
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  		Fig. 4. Water-soluble Zn dynamics during incubation of unamended and biosolids-amended soils. Error bars indicate standard deviation (n = 3).

 

Figure 5
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  		Fig. 5. Visual Minteq-calculated activities (µmol L–1) of the Zn-dissolved organic matter species on Days 0 and 23. Error bars indicate standard deviation (n = 3). Dissolved organic matter was assumed to have a molecular weight of 800 g mol–1 and a C content of 500 g kg–1.

 




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Copyright © 2007 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.