We studied a) leaching of Ulex, Pinus and Eucalyptus ashes; b) leachin
g from the surface layer (0 - 5 cm) of 6 types of soil subjected to th
ermal shock at a range of temperatures equivalent to those reached in
a wildfire (25-degrees-C to 700-degrees-C); and c) leaching of Ulex, P
inus and Eucalyptus ashes through a subsurface soil layer not subjecte
d to thermal shock. Element release from plant ashes and heat-treated
soils was highly dependent on the solubility of the principal chemical
forms in which that element occurred. The monovalent cations Na and K
, largely present as chlorides and carbonates, were mobilized much mor
e rapidly than the divalent cations Ca and Mg, largely present as oxid
es and carbonates. Element release from heat-treated soil was also dep
endent on shock temperature. The monovalent cations were extensively m
obilized following shocks at less than 380-degrees-C, and the divalent
cations following higher-temperature shocks. These differences appear
to be related to element volatilization and mineralization of organic
matter. The subsurface soil not subjected to thermal shock showed a t
endency to retain the elements released from plant ashes and from heat
-treated surface soil. The subsurface layers may also release hydrogen
ions and organic matter, as a result of cation exchange and dissoluti
on processes respectively.