5 research outputs found
Engineering Biogenic Magnetite for Sustained Cr(VI) Remediation in Flow-through Systems
In this work, we report a route to enhance the reactivity
and longevity
of biogenic magnetite in Cr(VI) remediation under continuous-flow
conditions by combining functionalization of the biomagnetite surface
with a precious metal catalyst, nanoscale palladium, and exposure
to formate. Column influent conditions were varied to simulate oxic,
anoxic, and nitrate cocontaminated environments. The addition of sodium
formate as an electron donor for Pd-functionalized magnetite increased
capacity and longevity allowing 80% removal of Cr(VI) after 300 h
in anoxic conditions, whereas complete breakthrough occurred after
60 h in anoxic nonformate and nonfunctionalized systems. Removal of
Cr(VI) was optimized under anoxic conditions, and the presence of
oxidizing agents results in a modest loss in reductive capacity. Examination
of reacted Pd-functionalized magnetite reveals close association of
Fe with Cr, suggesting that Pd-coupled oxidation of formate serves
to regenerate the reactive surface. XMCD studies revealed that Cr(III)
is partially substituted for Fe in the magnetite structure, which
serves to immobilize Cr. No evidence for a mechanistic interference
by nitrate cocontamination was observed, suggesting that this novel
system could provide robust, effective and sustained reduction of
contaminants, even in the presence of common oxidizing cocontaminants,
outperforming the reductive capacity of nonfunctionalized biogenic
magnetite
Engineering a Biometallic Whole Cell Catalyst for Enantioselective Deracemization Reactions
The ability of microbial cells to synthesize highly reactive nanoscale functional materials provides the basis for a novel synthetic biology tool for developing the next generation of multifunctional industrial biocatalysts. Here, we demonstrate that aerobic cultures of Escherichia coli, genetically engineered to overproduce a recombinant monoamine oxidase possessing high enantioselectivity against chiral amines, can be augmented with nanoscale Pd(0) precipitated via bioreduction reactions. The result is a novel biometallic catalyst for the deracemization of racemic amines. This deracemization process is normally achieved by discrete sequential oxidation/reduction steps using a separate enantiomer-specific biocatalyst and metal catalyst, respectively. Here, use of E. coli cultures carrying the cloned monoamine oxidase gene and nanoscale bioreduced Pd(0) particles was used successfully for the conversion of racemic 1-methyltetrahydroisoquinoline (MTQ) to (<i>R</i>)-MTQ, via the intermediate 1-methyl-3,4-dihydroisoquinoline, with an enantiomeric excess of up to 96%. There was no loss of catalyst activity following the five rounds of oxidation and reduction, and importantly, there was minimal loss of palladium into the reaction supernatant. This first demonstration of a whole cell biometallic catalyst mixture for “single-pot”, multistep reactions opens up the way for a wide range of integrated processes, offering a scalable and highly flexible platform technology
Redox Interactions Between Cr(VI) and Fe(II) in Bioreduced Biotite and Chlorite
Contamination
of the environment with Cr as chromate (Cr(VI)) from
industrial activities is of significant concern as Cr(VI) is a known
carcinogen, and is mobile in the subsurface. The capacity of Fe(II)-containing
phyllosilicates including biotite and chlorite to alter the speciation,
and thus the mobility, of redox-sensitive contaminants including Cr(VI)
is of great interest since these minerals are common in soils and
sediments. Here, the capacity of bacteria, ubiquitous in the surface
and near-surface environment, to reduce Fe(III) in phyllosilicate
minerals and, thus, alter their redox reactivity was investigated
in two-step anaerobic batch experiments. The model Fe(III)-reducing
bacterium <i>Geobacter sulfurreducens</i> was used to reduce
Fe(III) in the minerals, leading to a significant transformation of
structural Fe(III) to Fe(II) of 0.16 mmol/g (∼40%) in biotite
and 0.15 mmol/g (∼20%) in chlorite. The unaltered minerals
could not remove Cr(VI) from solution despite containing a larger
excess of Fe(II) than would be required to reduce all the added Cr(VI),
unless they were supplied in a very high concentration (a 1:10 solid
to solution ratio). By contrast, even at very low concentrations,
the addition of bioreduced biotite and chlorite caused removal of
Cr(VI) from solution, and surface and near surface X-ray absorption
spectroscopy confirmed that this immobilization was through reductive
transformation to Cr(III). We provide empirical evidence that the
amount of Fe(II) generated by microbial Fe(III) reduction is sufficient
to reduce the Cr(VI) removed and, in the absence of reduction by the
unaltered minerals, suggest that only the microbially reduced fraction
of the iron in the minerals is redox-active against the Cr(VI)
Microbial Reduction of Arsenic-Doped Schwertmannite by <i>Geobacter sulfurreducens</i>
The fate of As(V) during microbial reduction by <i>Geobacter
sulfurreducens</i> of Fe(III) in synthetic arsenic-bearing schwertmannites
has been investigated. During incubation at pH7, the rate of biological
Fe(III) reduction increased with increasing initial arsenic concentration.
From schwertmannites with a relatively low arsenic content (<0.3
wt %), only magnetite was formed as a result of dissimilatory iron
reduction. However, bioreduction of schwertmannites with higher initial
arsenic concentrations (>0.79 wt %) resulted in the formation of
goethite.
At no stage during the bioreduction process did the concentration
of arsenic in solution exceed 120 μgL<sup>1</sup>, even for
a schwertmannite with an initial arsenic content of 4.13 wt %. This
suggests that the majority of the arsenic is retained in the biominerals
or by sorption at the surfaces of newly formed nanoparticles.Subtle differences in the As <i>K</i>-edge XANES spectra
obtained from biotransformation products are clearly related to the
initial arsenic content of the schwertmannite starting materials.
For products obtained from schwertmannites with higher initial As
concentrations, one dominant population of As(V) species bonded to
only two Fe atoms was evident. By contrast, schwertmannites with relatively
low arsenic concentrations gave biotransformation products in which
two distinctly different populations of As(V) persisted. The first
is the dominant population described above, the second is a minority
population characterized by As(V) bonded to four Fe atoms. Both XAS
and XMCD evidence suggest that the latter form of arsenic is that
taken into the tetrahedral sites of the magnetite.We conclude
that the majority population of As(V) is sorbed to
the surface of the biotransformation products, whereas the minority
population comprises As(V) incorporated into the tetrahedral sites
of the biomagnetite. This suggests that microbial reduction of highly
bioavailable As(V)-bearing Fe(III) mineral does not necessarily result
in the mobilization of the arsenic
A One-Pot Synthesis of Monodispersed Iron Cobalt Oxide and Iron Manganese Oxide Nanoparticles from Bimetallic Pivalate Clusters
Monodispersed iron cobalt oxide (Fe<sub>2</sub>CoO<sub>4</sub>)
and iron manganese oxide (Mn<sub>0.43</sub>Fe<sub>2.57</sub>O<sub>4</sub>) nanoparticles have been synthesized using bimetallic pivalate
clusters of [Fe<sub>2</sub>CoO(O<sub>2</sub>C<sup>t</sup>Bu)<sub>6</sub>(HO<sub>2</sub>C<sup>t</sup>Bu)<sub>3</sub>] (<b>1</b>), Co<sub>4</sub>Fe<sub>2</sub>O<sub>2</sub>(O<sub>2</sub>C<sup>t</sup>Bu)<sub>10</sub>(MeCN)<sub>2</sub>] (<b>2</b>), and [Fe<sub>2</sub>MnO(O<sub>2</sub>C<sup>t</sup>Bu)<sub>6</sub>(HO<sub>2</sub>C<sup>t</sup>Bu)<sub>3</sub>] (<b>3</b>) respectively as single source
precursors. The precursors were thermolyzed in a mixture of oleylamine
and oleic acid with either diphenyl ether or benzyl ether as solvent
at their respective boiling points of 260 or 300 °C. The effect
of reaction time, temperature and precursor concentration (0.25 or
0.50 mmol) on the stoichiometry, phases or morphology of the nanoparticles
were studied. TEM showed that highly monodispersed spherical nanoparticles
of Fe<sub>2</sub>CoO<sub>4</sub> (3.6 ± 0.2 nm) and Mn<sub>0.43</sub>Fe<sub>2.57</sub>O<sub>4</sub> (3.5 ± 0.2 nm) were obtained
from 0.50 mmol of <b>1</b> or <b>3</b>, respectively at
260 °C. The decomposition of the precursors at 0.25 mmol and
300 °C revealed that larger iron cobalt oxide or iron manganese
oxide nanoparticles were obtained from <b>1</b> and <b>3</b>, respectively, whereas the opposite was observed for iron cobalt
oxide from <b>2</b> as smaller nanoparticles appeared. The reaction
time was investigated for the three precursors at 0.25 mmol by withdrawing
aliquots at 5 min, 15 min, 30 min, 1 h, and 2 h. The results obtained
showed that aliquots withdrawn at reaction times of less than 1 h
contain traces of iron oxide, whereas only pure cubic iron cobalt
oxide or iron manganese oxide was obtained after 1 h. Magnetic measurements
revealed that all the nanoparticles are superparamagnetic at room
temperature with high saturation magnetization values. XMCD confirmed
that in iron cobalt oxide nanoparticles, most of the Co<sup>2+</sup> cations are in the octahedral site. There is also evidence in the
magnetic measurements for considerable hysteresis (>1T) observed
at
5 K. EPMA analysis and ICP-OES measurements performed on iron cobalt
oxide nanoparticles obtained from [Fe<sub>2</sub>CoO(O<sub>2</sub>C<sup>t</sup>Bu)<sub>6</sub>(HO<sub>2</sub>C<sup>t</sup>Bu)<sub>3</sub>] <b>(1)</b> revealed that stoichiometric Fe<sub>2</sub>CoO<sub>4</sub> was obtained only for 0.50 mmol precursor concentration.
All the nanoparticles were characterized by powder X-ray diffraction
(p-XRD), transmission electron microscopy (TEM), inductively coupled
plasma-optical emission spectroscopy (ICP-OES), electron probe microanalysis
(EPMA), X-ray magnetic circular dichroism (XMCD), and superconducting
quantum interference device (SQUID) magnetometry