The formation and
transformation of schwertmannite affect the migration,
conversion, and toxicity of chromium (Cr) in soils and sediments.
Schwertmannite could be obtained from the oxidation of Fe(II) by hydroxyl
radicals (OH•) and superoxide radicals (O2•–) generated from the photolysis of NO3– under acidic and sulfate-rich conditions.
As one of the most abundant components, montmorillonite is widely
distributed in soils and sediments. However, the effect of montmorillonite
on the photochemical formation process and corresponding Cr adsorption
behaviors of schwertmannite remains elusive. This study indicates
that schwertmannite could be formed on the montmorillonite surface
during the photocatalytic oxidation of dissolved Fe(II). The formation
rate, particle size, and crystallinity degree of schwertmannite formed
on montmorillonite surface increased with increasing FeSO4 concentration (1.0–5.0 mmol L–1). The presence
of montmorillonite led to a decrease in the particle size of schwertmannite.
When the initial concentration of Fe(II) was 5.0 mmol L–1, the specific surface area of schwertmannite–montmorillonite
aggregates reached 243.3 m2 g–1, which
was remarkably larger than that of single-phase schwertmannite (24.6
m2 g–1) and montmorillonite (138.1 m2 g–1). The schwertmannite–montmorillonite
aggregates showed a higher adsorption capacity for Cr(VI) (97.4 mg
Cr g–1 Fe) than single-phase schwertmannite (72.9
mg Cr g–1 Fe). This work reveals the possible formation
pathway and Cr adsorption behavior of schwertmannite on the surface
of montmorillonite in waters and soils.