Abstract

Sequential reduction processes were studied in four oxic upland soils (cultivated, forest, savanna and desert soil) which were slurried and incubated under anoxic conditions. NO 3 −1 reduction began almost immediately and was followed by reduction of manganese(IV), sulfate and iron(III). The phases of reduction of Mn 4+, SO 4 2− and Fe 3+ overlapped, with SO 4 2− being depleted long before accumulation of Mn 2+ and Fe 2+ was finished. CH 4 production and growth of methanogenic bacteria began when all the other reduction processes were finished. Radiotracer experiments showed that CH 4 was produced from H 2 (29–42%) and acetate. The respiratory index indicated that the acetate was predominantly degraded by methanogenic bacteria. The late onset of methanogenesis was not a consequence of limitation by the methanogenogenic precursors, since H 2 and acetate were present long before the initiation of methanogenesis. Thermodynamic calculations showed that the concentrations of these substrates were always sufficient to allow exergonic production of CH 4 at Gibbs free energies of ΔG < −30 kJ mol −1 CH 4. However, exergonic production of acetate from H 2 CO 2 was not possible. Propionate was also detected in the soil slurries. The redox potential in the soils decreased from > + 400 mV to final values of < − 150 mV, except in the forest soil where the redox potential stayed at + 50 mV. The onset of methanogenesis and of growth of methanogenic bacteria coincided with redox potentials between +70 and 0 mV, which is much higher than claimed in literature. We speculate that the redox-active substances in soil were the signal for methanogenic bacteria to initiate activity.

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