The fate of chromium in the environment
relies heavily on its redox
chemistry and interaction with iron oxide surfaces. Atomic layer deposition
was used to deposit a 10 nm film of polycrystalline α-Fe2O3 (hematite) onto a fused silica substrate which
was analyzed using second harmonic generation (SHG), a coherent, surface-specific,
nonlinear optical technique. Specifically, the χ(3) technique was used to investigate the adsorption of Cr(III) and
Cr(VI) to the hematite/water interface under flow conditions at pH
4 with 10 mM NaCl. We observed partially irreversible adsorption of
Cr(III), the extent of which was found to be dependent on the concentration
of Cr(III) ions in solution. This result was confirmed using X-ray
photoelectron spectroscopy. The interaction of Cr(III) with hematite
is compared with the adsorption of Cr(III) to the silica/water interface,
which is the substrate for the ALD-prepared hematite films, and found
to be fully reversible under the same experimental conditions. The
observed binding constant for Cr(III) interacting with the silica
surface was found to be 4.0(6) × 103 M–1, which corresponds to an adsorption free energy of −30.5(4)
kJ/mol when referenced to 55.5 M water. The surface charge density
at maximum metal ion surface coverage was found to be 0.005(1) C/m2, which corresponds to 1.0 × 1012 ions/cm2 assuming a +3 charge for chromium. In contrast, the observed
binding constant for Cr(III) interacting reversibly with the hematite
surface was calculated to be 2(2) × 104 M–1, corresponding to an adsorption free energy of −35(2) kJ/mol
when referenced to 55.5 M water. The surface charge density at maximum
metal ion surface coverage was found to be 0.004(5) C/m2 for the reversibly bound chromium species, which corresponds to
8.3 × 1011 reversibly bound ions per cm2, again assuming a +3 charge of chromium. The data also allows us
to estimate that about 6.7 × 1012 Cr(III) ions are
irreversibly bound per cm2 hematite at saturation coverage.
The results of this investigation suggest that the use of hematite
in permeable reactive barriers, for cost-effective chromium remediation,
allows for Cr(III) remediation at very low concentrations through
adsorptive and redox processes but quickly renders the barriers ineffective
at high chromium concentrations due to surface saturation.