There are reports that nano-sized zero-valent iron (Fe0)
exhibits greater reactivity than micro-sized particles of
Fe0, and it has been suggested that the higher reactivity
of nano-Fe0 may impart advantages for groundwater
remediation or other environmental applications. However,
most of these reports are preliminary in that they leave
a host of potentially significant (and often challenging) material
or process variables either uncontrolled or unresolved.
In an effort to better understand the reactivity of nano-Fe0, we have used a variety of complementary techniques
to characterize two widely studied nano-Fe0 preparations:
one synthesized by reduction of goethite with heat and H2
(FeH2) and the other by reductive precipitation with
borohydride (FeBH). FeH2 is a two-phase material consisting
of 40 nm α-Fe0 (made up of crystals approximately the
size of the particles) and Fe3O4 particles of similar size or
larger containing reduced sulfur; whereas FeBH is mostly
20−80 nm metallic Fe particles (aggregates of <1.5 nm grains)
with an oxide shell/coating that is high in oxidized
boron. The FeBH particles further aggregate into chains.
Both materials exhibit corrosion potentials that are more
negative than nano-sized Fe2O3, Fe3O4, micro-sized Fe0, or a
solid Fe0 disk, which is consistent with their rapid reduction
of oxygen, benzoquinone, and carbon tetrachloride.
Benzoquinonewhich presumably probes inner-sphere
surface reactionsreacts more rapidly with FeBH than FeH2,
whereas carbon tetrachloride reacts at similar rates
with FeBH and FeH2, presumably by outer-sphere electron
transfer. Both types of nano-Fe0 react more rapidly than micro-sized Fe0 based on mass-normalized rate constants, but
surface area-normalized rate constants do not show a
significant nano-size effect. The distribution of products
from reduction of carbon tetrachloride is more favorable with
FeH2, which produces less chloroform than reaction with
FeBH.
The gas-phase photooxidation of trichloroethylene (TCE) on
Pt/TiO2 has been investigated. The
wavelength
dependence of this reaction on Pt/TiO2 shows that the
addition of small amounts of platinum (≤2%) to
TiO2
can enhance the photooxidation of TCE to much longer wavelengths.
This result correlates with Maxwell−Garnett calculations and experimental absorption curves for
Pt/TiO2 samples. Although the spectral
response
of Pt/TiO2 extends to longer wavelengths,
Pt/TiO2 is found to be less effective in the photooxidation
of
gas-phase TCE upon broad-band irradiation (λ > 300 nm) compared to
TiO2. It is proposed that site blocking
by the Pt particles of the most active sites, Ti3+ sites,
is the cause of the decreased photoactivity. In
addition,
it has also been determined that the photoproduct distribution changes
as a function of platinum loading.
Mechanisms to explain the observed effects of Pt loading on the
photooxidation of TCE on Pt/TiO2 are
discussed.
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