Manganese (Mn) exists as Mn(II), Mn(III), or Mn(IV) in
soils, and
the Mn oxidation state controls the roles of Mn in numerous environmental
processes. However, the variations of Mn oxidation states with climate
remain unknown. We determined the Mn oxidation states in highly weathered
bulk volcanic soils (primary minerals free) across two rainfall gradients
covering mean annual precipitation (MAP) of 0.25–5 m in the
Hawaiian Islands. With increasing MAP, the soil redox conditions generally
shifted from oxic to suboxic and to anoxic despite fluctuating at
each site; concurrently, the proportions of Mn(IV) and Mn(II) decreased
and increased, respectively. Mn(III) was low at both low and high
MAP, but accumulated substantially, up to 80% of total Mn, in soils
with prevalent suboxic conditions at intermediate MAP. Mn(III) was
likely hosted in Mn(III,IV) and iron(III) oxides or complexed with
organic matter, and its distribution among these hosts varied with
soil redox potentials and soil pH. Soil redox conditions and rainfall-driven
leaching jointly controlled exchangeable Mn(II) in soils, with its
concentration peaking at intermediate MAP. The Mn redox chemistry
was at disequilibrium, with the oxidation states correlating with
long-term average soil redox potentials better than with soil pH.
The soil redox conditions likely fluctuated between oxic and anoxic
conditions more frequently at intermediate than at low and high MAP,
creating biogeochemical hot spots where Mn, Fe, and other redox-sensitive
elements may be actively cycled.