The cycling of common sorbents such as metal (hydr)oxides, carbonates, and
sulfides in redox-active environments influences the partitioning of associ
ated trace elements such as zinc. Consequently, fluctuations in redox statu
s may in part determine the availability and mobility of Zn and other trace
elements. This research examines changes in Zn speciation in a contaminate
d wetland soil that undergoes seasonal flooding. X-ray absorption spectrosc
opy (XAS) was employed to identify and quantify Zn species from soil cores
collected over a 1-year cycle as a function of water depth, location, and s
oil depth. Zinc associated with (hydr)oxide phases in dry, oxidized soils a
nd with sulfides and carbonates in flooded systems. An increase in water le
vel was accompanied by a reversible change in Zn fractionation toward ZnS a
nd ZnCO3. However, a small, recalcitrant fraction of Zn associated with (hy
dr)oxides remained even when the soils were exposed to highly reducing cond
itions. Water depth and redox potential were the most important factors in
determining Zn speciation, although spatial variation was also important. T
hese data indicate that zinc sorption is a dynamic process influenced by en
vironmental changes.