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Compost and Calcium Surface Treatment Effects on Subsoil Chemistry in Acidic Minespoil Columns

Frank J. von Willert and Richard C. Stehouwer*

Department of Crop and Soil Sciences, Penn State Univ., 116 ASI Building, University Park, PA 16802



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Fig. 1. Cumulative dissolved organic carbon (DOC) leaching, calculated from the leachates collected at the bottom of the columns. Values are means of three replicates ± standard deviation. N, no Ca added; G, gypsum; L, CaCO3; LG, CaCO3 + gypsum; c0, no compost added (values for N, G, L, LG all fell on this line); cm, 34.4 g kg-1 compost; ch, 68.8 g kg-1 compost.

 


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Fig. 2. Cumulative leaching of Ca (left panel) and Al (right panel) calculated from the leachates collected at the bottom of the columns. Values are means of three replicates ± standard deviation. N, no Ca added; G, gypsum; L, CaCO3; LG, CaCO3 + gypsum; c0, no compost; cm, 34.4 g kg-1 compost; ch, 68.8 g kg-1 compost.

 


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Fig. 3. Solubility diagram for jurbanite [AlSO4(OH)·5H2O], alunite [KAl3(SO4)2(OH)6], basaluminite [Al4(OH)10SO4·17H2O], and diaspore (AlOOH). The Al3+ activities were calculated from the measured Al concentration, accounting for the formation of Al–SO4 complexes. Thermodynamic data are taken from Lindsay and Walthall (1996). Lines are calculated by assuming log = -1.83. Error bars are for log = -0.83 and log = -2.83. For alunite we assumed log(K+) = -5.6. Black dots represent measured data.

 





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