V. Peters et R. Conrad, SEQUENTIAL REDUCTION PROCESSES AND INITIATION OF CH4 PRODUCTION UPON FLOODING OF OXIC UPLAND SOILS, Soil biology & biochemistry, 28(3), 1996, pp. 371-382
Sequential reduction processes were-Studied in four oxic upland soils
(cultivated, forest, savanna and desert soil) which were slurried and
incubated under anoxic conditions. NO3- reduction began almost immedia
tely and was followed by reduction of manganese(IV), sulfate and iron(
III). The phases of reduction of Mn4+, SO42- and Fe3+ overlapped, with
SO42- being depleted long before accumulation of Mn2+ and Fe2+ was fi
nished. CH4 production and growth of methanogenic bacteria began when
all the other reduction processes were finished. Radiotracer experimen
ts showed that CHI was produced from H-2 (29-42%) and acetate. The res
piratory index indicated that the acetate was predominantly degraded b
y methanogenic bacteria. The !ate onset of methanogenesis was not a co
nsequence 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 su
bstrates were always sufficient to allow exergonic production of CH4 a
t Gibbs free energies of Delta G < - 30 kJ mol(-1) CH4. However, exerg
onic production of acetate from H-2/CO2 was not possible. Propionate w
as also detected in the soil slurries. The redox potential in the soil
s decreased from > + 400 mV to final values of < - 150 mV, except in t
he forest soil where the redox potential stayed at + 50 mV. The onset
of methanogenesis and of growth of methanogenic bacteria coincided wit
h redox potentials between + 70 and 0 mV, which is much higher than cl
aimed in the literature. We speculate that the redox-active substances
in soil were the signal for methanogenic bacteria to initiate activit
y.