8 research outputs found
CO Oxidation Over Au/TiO\u3csub\u3e2\u3c/sub\u3e Catalyst: Pretreatment Effects, Catalyst Deactivation, and Carbonates Production
A commercially available Au/TiO2 catalyst was subjected to a variety of thermal treatments in order to understand how variations in catalyst pretreatment procedures might affect CO oxidation catalysis. Catalytic activity was found to be inversely correlated to the temperature of the pretreatment. Infrared spectroscopy of adsorbed CO experiments, followed by a Temkin analysis of the data, indicated that the thermal treatments caused essentially no changes to the electronics of the Au particles; this, and a series of catalysis control experiments, and previous transmission electron microscopy (TEM) studies ruled out particle growth as a contributing factor to the activity loss. Fourier transform infrared (FTIR) spectroscopy showed that pretreating the catalyst results in water desorption from the surface, but the observable water loss was similar for all the treatments and could not be correlated with catalytic activity. A Michaelis–Menten kinetic treatment indicated that the main reason for deactivation is a loss in the number of active sites with little changes in their intrinsic activity. In situ FTIR experiments during CO oxidation showed extensive buildup of carbonate-like surface species when the pretreated catalysts were contacted with the feed gas. A semi-quantitative infrared spectroscopy method was developed for comparing the amount of carbonates present on each catalyst; results from these experiments showed a strong correlation between the steady-state catalytic activity and amount of surface carbonates generated during the initial moments of catalysis. Further, this experimental protocol was used to show that the carbonates reside on the titania support rather than on the Au, as there was no evidence that they poison Au–CO binding sites. The role of the carbonates in the reaction scheme, their potential role in catalyst deactivation, and the role of surface hydroxyls and water are discussed
Laser-Induced Graphene Capacitive Killing of Bacteria
Laser-induced graphene (LIG) is a
method of generating a foam-like
conformal carbon layer of porous graphene on many types of carbon-based
surfaces. This electrically conductive material has been shown to
be useful in many applications including environmental technology
and includes low fouling and antimicrobial surfaces and can address
persistent environmental challenges spawned by bacterial and viral
contaminates. Here, we show that a single film of LIG stores charge
when an electrical current is applied and dissipates charge when the
current is stopped, which results in electricidal surface antibacterial
potency. The amount of accumulated and dissipated charge on a single
strip of LIG was quantified with an electrometer by generating LIG
on both sides of a nonconducting polyimide film, which showed up to
65 pC of charge when the distance between the surfaces was 94 μm
corresponding to an areal capacitance of 1.63 pF/cm2. We
further corroborate the stored charge decay of a single LIG strip
with bacteria death via direct electrical contact. Antimicrobial rates
decreased with the same monotonic pattern as the loss of charge from
the LIG film (i.e., AR ∼ 97% 0 s after voltage source disconnection
vs AR ∼ 21% 90 s after disconnection) showing bacterial death
as a function of delayed LIG exposure time after applied voltage disconnection.
In terms of energy efficiency, this translates to an increased bacteria
potency of ∼170% for the equivalent energy costs as that previously
estimated. Finally, we present a mechanistic explanation for the capacitive
behavior and the electricidal effects for a single plate of LIG
Laser-Induced Graphene Capacitive Killing of Bacteria
Laser-induced graphene (LIG) is a
method of generating a foam-like
conformal carbon layer of porous graphene on many types of carbon-based
surfaces. This electrically conductive material has been shown to
be useful in many applications including environmental technology
and includes low fouling and antimicrobial surfaces and can address
persistent environmental challenges spawned by bacterial and viral
contaminates. Here, we show that a single film of LIG stores charge
when an electrical current is applied and dissipates charge when the
current is stopped, which results in electricidal surface antibacterial
potency. The amount of accumulated and dissipated charge on a single
strip of LIG was quantified with an electrometer by generating LIG
on both sides of a nonconducting polyimide film, which showed up to
65 pC of charge when the distance between the surfaces was 94 μm
corresponding to an areal capacitance of 1.63 pF/cm2. We
further corroborate the stored charge decay of a single LIG strip
with bacteria death via direct electrical contact. Antimicrobial rates
decreased with the same monotonic pattern as the loss of charge from
the LIG film (i.e., AR ∼ 97% 0 s after voltage source disconnection
vs AR ∼ 21% 90 s after disconnection) showing bacterial death
as a function of delayed LIG exposure time after applied voltage disconnection.
In terms of energy efficiency, this translates to an increased bacteria
potency of ∼170% for the equivalent energy costs as that previously
estimated. Finally, we present a mechanistic explanation for the capacitive
behavior and the electricidal effects for a single plate of LIG
CO Adsorption on Au/TiO<sub>2</sub> Catalysts: Observations, Quantification, and Explanation of a Broad-Band Infrared Signal
The adsorption of CO on Au/TiO<sub>2</sub> catalysts was examined
at room temperature using FTIR transmission spectroscopy. Adsorption
was observed as (i) a sharp peak at ∼2100 cm<sup>–1</sup> due to CO molecular vibration (the Au–CO peak), and (ii)
a broad-band infrared (BB-IR) signal. The Au–CO peak and BB-IR
signal are correlated and quantitatively related to the amount of
CO adsorbed on the Au nanoparticles. For comparison purposes, we also
examined CO adsorption on Au/Al<sub>2</sub>O<sub>3</sub> catalysts.
When supported on this nonreducible support, CO adsorption on Au showed
only the Au–CO peak; the BB-IR signal was absent. This allowed
us to determine that the BB-IR signal observed for CO adsorption on
the Au/TiO<sub>2</sub> catalyst is associated with the reducibility
of the support. Comparison of the two catalysts also enabled us to
determine that the BB-IR signal is due to a decrease in transmission
through the powdered catalysts when CO adsorbs on Au/TiO<sub>2</sub>. Consistent with previously published studies, we propose that this
BB-IR signal is related to the reversible, partial reduction of the
TiO<sub>2</sub> at the Au–TiO<sub>2</sub> interface. This reduction
leads to an increase in surface disorder or roughening of TiO<sub>2</sub> particles that produces a decrease in IR transmission through
the catalyst (i.e. an increase in IR scattering). These results suggest
an efficient CO–Au–TiO<sub>2</sub> adsorbate-induced
electronic metal–support interaction (EMSI) that may play an
important role in understanding CO reactions on Au/TiO<sub>2</sub> catalysts
Superparamagnetic nanoadsorbents for the removal of trace As(III) in drinking water
A series of novel zeolitic imidazolate framework (ZIF) decorated superparamagnetic graphene oxide hybrid nanoadsorbents were synthesized, characterized, and tested for their As(III) adsorbed amount in simulated drinking water. The three composite nanomaterials are based each on three isostructural and water stable ZIFs, (C-1 based on ZIF-8, C-2 based on ZIF-67, and C-3 based on ZIF-Zn/Co). The composite nanomaterials and there parent materials were characterized through pXRD, TEM, FTIR, BET and magnetometry methods (SQUID), and were tested as adsorbents in a representative drinking water matrix containing arsenite (As(III)) at an initial trace concentration (realistic in some natural drinking water sources) of 35 µg/L. The nanoadsorbents were magnetically captured and removed after adsorption in batch conditions. Out of the three composites, C-2 shows the highest As(III) adsorbed amount at an initial concentration of 35 µg/L (q0) of 202 µg/g, followed by C-3 with 102 µg/g and C-1 with 82 µg/g