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Published online 1 January 2007
Published in Soil Sci Soc Am J 71:64-74 (2007)
DOI: 10.2136/sssaj2006.0111
© 2007 Soil Science Society of America
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Precipitation of Dissolved Organic Matter by Aluminum Stabilizes Carbon in Acidic Forest Soils

T. Scheel*, C. Dörfler and K. Kalbitz

Dep. of Soil Ecology, Bayreuth Center of Ecology and Environ., Research (BayCEER), Univ. of Bayreuth, D-95440 Bayreuth, Germany


Figure 1
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Fig. 1. Specific ultraviolet (UV) absorption at 2 0 nm of the extracted dissolved organic matter solutions from the oa and oi horizons of a beech and a spruce forest in relation to their aromatic c content, determined by­ solution 1 c nuclear magnetic resonance.

 

Figure 2
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Fig. 2. The maximum percentage of dissolved organic C precipitated from the dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest (at pH 4.5 and Al/C ratio of 0.3, except for the Oi-spruce solution, which had an Al/C ratio of 0.1) after Al addition in relation to the content of aromatic C and aromatic H.

 

Figure 3
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Fig. 3. The Al/C ratios in precipitates (solid phase) of the dissolved organic matter (DOM) solutions from the Oa and Oi horizons of a beech and a spruce forest in relation to the initially adjusted Al/C ratios in the DOM solutions. Precipitation was initiated at two different pH values: pH 3.8 (left) and pH 4.5 (right). Mean values and standard error of three replicates.

 

Figure 4
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Fig. 4. Ratio of Al needed to precipitate similar amounts of dissolved organic C at pH 4.5 and 3.8 (dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest, different Al/C ratios). Ratios >1 mean that more Al was necessary at pH 4.5 to precipitate the same amount of C as at pH 3.8.

 

Figure 5
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Fig. 5. Specific ultraviolet (UV) absorption (280 nm) of initial dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest (Al/C ratio 0) and after removal of precipitates by filtration. Precipitation was initiated at two pH values and four different Al/C ratios. Mean values and standard error of three replicates.

 

Figure 6
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Fig. 6. Aromatic C content of initial dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest (Al/C ratio 0) and of precipitates for two pH values and four Al/C ratios. Mean values and standard error of three replicates.

 

Figure 7
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Fig. 7. Organic C/organic N ratios of initial dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest (Al/C ratio 0) and of precipitates for two pH values and four Al/C ratios. Mean values and standard error of three replicates.

 

Figure 8
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Fig. 8. Dynamics of C mineralization of Al–organic matter (OM) precipitates (as a percentage of initial C) during 7 wk of incubation at pH 4.5 and 20°C. The Al–OM precipitates were produced from dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest at two pH values and four Al/C ratios. Mean values and standard error of three replicates.

 

Figure 9
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Fig. 9. Mineralization of Al–organic matter precipitates (Al/C ratio 0.1) produced from dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest at pH 3.8 and 4.5 (incubation at pH 4.5 and 20°C for 7 wk). Mean values and standard error of three replicates.

 

Figure 10
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Fig. 10. Mineralization of Al–organic matter precipitates (from dissolved organic matter solutions from the Oa and Oi horizons of a beech and a spruce forest) in dependence on the aromatic C content and the organic C/organic N ratio of the precipitates (multiple linear regression: R2 = 0.76; dissolved organic carbon [DOC] mineralized [as a percentage of initial DOC] = 9.992 – 0.091(C/N ratio) – 0.161(aromatic C) [%]).

 





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