Previous research has indicated that heavy metals, including Mn, are d
istributed unevenly within soil aggregates. Reducing conditions at the
onset of the rainy season in Costa Rica may lead to a redistribution
of Mn between aggregate interior and exterior. The objective of this p
aper is to examine differences in redox dynamics of Mn between aggrega
te interior, exterior and bulk soil in a Typic Haplustalf. From April
4 to June 26, redox potential was measured in depths of 10 and 35 cm w
ith permanently installed Pt-electrodes. Aggregates and bulk soil were
collected every 2 weeks at depths of 0-10 and 30-40 cm. Soil aggregat
es were separated mechanically into interior and exterior. In the aggr
egate fractions we measured Mn concentrations, which were speciated wi
th a 4-step sequential extraction procedure. Although the redox potent
ial dropped only slightly from April to July, Mn was reduced first in
the aggregate exterior and later in the aggregate interior. The ratio
of mobile Mn in the exterior to that in the interior reached 7 in the
topsoil and 15 in the subsoil on May 16. At that time, mobile Mn conce
ntrations in the topsoil were 193 mg kg(-1) in the exterior. The bulk
soil, consisting of soil aggregates and nonaggregated soil material be
tween aggregates, showed a decrease in mobile Mn during the whole stud
y period. This was probably attributable to increased leaching and pla
nt uptake. These seasonal Mn dynamics are important for plant Mn nutri
tion and may also play a crucial role in heavy metal mobilization caus
ed by the high heavy metal sorption capacity of Mn oxides.