Speciation plays an important role in determining the overall leachability
of selenium in soil. In this study we present a mathematical model and resu
lts of miscible displacement experiments that were conducted to evaluate si
multaneous reduction and transport of selenate in saturated soil columns. T
he experiments were carried out in organic amended (compost manure or glute
n) or unamended soil, with O-2-sparged or nonsparged influent solution. In
all columns, reduction of selenate was fast enough to produce selenite flux
in the effluent and elemental Se in the soil profile during a mean residen
ce time of similar to 30 hours. Reduction was accelerated in the presence o
f organic amendments and under low O-2 concentrations, resulting in an incr
eased retardation of selenium transport as a whole. The results of our expe
riments show that although selenate does not sorb to solid surfaces during
transport, it reduces rapidly to forms that are strongly retarded. On the b
asis of simulation with the consecutive reaction and transport model using
parameters derived from this study, selenium is expected to be retained nea
r the soil surface, even under extreme leaching conditions.