6 research outputs found
Ferrate(VI)-Induced Arsenite and Arsenate Removal by In Situ Structural Incorporation into Magnetic Iron(III) Oxide Nanoparticles
We
report the first example of arsenite and arsenate removal from
water by incorporation of arsenic into the structure of nanocrystalline
iron(III) oxide. Specifically, we show the capability to trap arsenic
into the crystal structure of γ-Fe<sub>2</sub>O<sub>3</sub> nanoparticles
that are in situ formed during treatment of arsenic-bearing water
with ferrate(VI). In water, decomposition of potassium ferrate(VI)
yields nanoparticles having core–shell nanoarchitecture with
a γ-Fe<sub>2</sub>O<sub>3</sub> core and a γ-FeOOH shell.
High-resolution X-ray photoelectron spectroscopy and in-field <sup>57</sup>Fe Mössbauer spectroscopy give unambiguous evidence
that a significant portion of arsenic is embedded in the tetrahedral
sites of the γ-Fe<sub>2</sub>O<sub>3</sub> spinel structure.
Microscopic observations also demonstrate the principal effect of
As doping on crystal growth as reflected by considerably reduced average
particle size and narrower size distribution of the “in-situ”
sample with the embedded arsenic compared to the “ex-situ”
sample with arsenic exclusively sorbed on the iron oxide nanoparticle
surface. Generally, presented results highlight ferrate(VI) as one
of the most promising candidates for advanced technologies of arsenic
treatment mainly due to its environmentally friendly character, in
situ applicability for treatment of both arsenites and arsenates,
and contrary to all known competitive technologies, firmly bound part
of arsenic preventing its leaching back to the environment. Moreover,
As-containing γ-Fe<sub>2</sub>O<sub>3</sub> nanoparticles are
strongly magnetic allowing their separation from the environment by
application of an external magnet
Air Stable Magnetic Bimetallic Fe–Ag Nanoparticles for Advanced Antimicrobial Treatment and Phosphorus Removal
We report on new magnetic bimetallic
Fe–Ag nanoparticles
(NPs) which exhibit significant antibacterial and antifungal activities
against a variety of microorganisms including disease causing pathogens,
as well as prolonged action and high efficiency of phosphorus removal.
The preparation of these multifunctional hybrids, based on direct
reduction of silver ions by commercially available zerovalent iron
nanoparticles (nZVI) is fast, simple, feasible in a large scale with
a controllable silver NP content and size. The microscopic observations
(transmission electron microscopy, scanning electron microscopy/electron
diffraction spectroscopy) and phase analyses (X-ray diffraction, Mössbauer
spectroscopy) reveal the formation of Fe<sub>3</sub>O<sub>4</sub>/γ-FeOOH
double shell on a “redox” active nZVI surface. This
shell is probably responsible for high stability of magnetic bimetallic
Fe–Ag NPs during storage in air. Silver NPs, ranging between
10 and 30 nm depending on the initial concentration of AgNO<sub>3</sub>, are firmly bound to Fe NPs, which prevents their release even during
a long-term sonication. Taking into account the possibility of easy
magnetic separation of the novel bimetallic Fe–Ag NPs, they
represent a highly promising material for advanced antimicrobial and
reductive water treatment technologies
Ferrate(VI)-Prompted Removal of Metals in Aqueous Media: Mechanistic Delineation of Enhanced Efficiency via Metal Entrenchment in Magnetic Oxides
The removal efficiency of heavy metal
ions (cadmium(II), Cd(II);
cobalt(II), Co(II); nickel(II), Ni(II); copper(II), Cu(II)) by potassium
ferrate(VI) (K<sub>2</sub>FeO<sub>4</sub>, Fe(VI)) was studied as
a function of added amount of Fe(VI) (or Fe) and varying pH. At pH
= 6.6, the effective removal of Co(II), Ni(II), and Cu(II) from water
was observed at a low Fe-to-heavy metal ion ratio (Fe/M(II) = 2:1)
while a removal efficiency of 70% was seen for Cd(II) ions at a high
Fe/Cd(II) weight ratio of 15:1. The role of ionic radius and metal
valence state was explored by conducting similar removal experiments
using Al(III) ions. The unique combination of X-ray diffraction (XRD),
X-ray photoelectron spectroscopy (XPS), in-field Mössbauer
spectroscopy, and magnetization measurements enabled the delineation
of several distinct mechanisms for the Fe(VI)-prompted removal of
metal ions. Under a Fe/M weight ratio of 5:1, Co(II), Ni(II), and
Cu(II) were removed by the formation of MFe<sub>2</sub>O<sub>4</sub> spinel phase and partially through their structural incorporation
into octahedral positions of γ-Fe<sub>2</sub>O<sub>3</sub> (maghemite)
nanoparticles. In comparison, smaller sized Al(III) ions got incorporated
easily into the tetrahedral positions of γ-Fe<sub>2</sub>O<sub>3</sub> nanoparticles. In contrast, Cd(II) ions either did not form
the spinel ferrite structure or were not incorporated into the lattic
of iron(III) oxide phase due to the distinct electronic structure
and ionic radius. Environmentally friendly removal of heavy metal
ions at a much smaller dosage of Fe than those of commonly applied
iron-containing coagulants and the formation of ferrimagnetic species
preventing metal ions leaching back into the environment and allowing
their magnetic separation are highlighted
Enhanced Oxidative and Adsorptive Removal of Diclofenac in Heterogeneous Fenton-like Reaction with Sulfide Modified Nanoscale Zerovalent Iron
Sulfidation of nanoscale zerovalent
iron (nZVI) has shown some
fundamental improvements on reactivity and selectivity toward pollutants
in dissolved-oxygen (DO)-stimulated Fenton-like reaction systems (DO/S-nZVI
system). However, the pristine microstructure of sulfide-modified
nanoscale zerovalent iron (S-nZVI) remains uncovered. In addition,
the relationship between pollutant removal and the oxidation of the
S-nZVI is largely unknown. The present study confirms that sulfidation
not only imparts sulfide and sulfate groups onto the surface of the
nanoparticle (both on the oxide shell and on flake-like structures)
but also introduces sulfur into the Fe(0) core region. Sulfidation
greatly inhibits the four-electron transfer pathway between Fe(0)
and oxygen but facilitates the electron transfer from Fe(0) to surface-bound
Fe(III) and consecutive single-electron transfer for the generation
of H<sub>2</sub>O<sub>2</sub> and hydroxyl radical. In the DO/S-nZVI
system, slight sulfidation (S/Fe molar ratio = 0.1) is able to nearly
double the oxidative removal efficacy of diclofenac (DCF) (from 17.8
to 34.2%), whereas moderate degree of sulfidation (S/Fe molar ratio
= 0.3) significantly enhances both oxidation and adsorption of DCF.
Furthermore, on the basis of the oxidation model of S-nZVI, the DCF
removal process can be divided into two steps, which are well modeled
by parabolic and logarithmic law separately. This study bridges the
knowledge gap between pollutant removal and the oxidation process
of chemically modified iron-based nanomaterials
Zero-Valent Iron Nanoparticles with Unique Spherical 3D Architectures Encode Superior Efficiency in Copper Entrapment
The
large-scale preparation of spherical condensed-type superstructures
of zero-valent iron (nZVI), obtained by controlled solid-state reaction
through a morphologically conserved transformation of a magnetite
precursor, is herein reported. The formed 3D nanoarchitectures (S-nZVI)
exhibit enhanced entrapment efficiency of heavy metal pollutants,
such as copper, compared to all previously tested materials reported
in the literature, thus unveiling the relevance in the material’s
design of the morphological variable. The superior removal efficiency
of these mesoporous S-nZVI superstructures is linked to their extraordinary
ability to couple effectively processes such as reduction and sorption
of the metal pollutant
Sulfidation of Iron-Based Materials: A Review of Processes and Implications for Water Treatment and Remediation
Iron-based
materials used in water treatment and groundwater remediationespecially
micro- and nanosized zerovalent iron (nZVI)can be more effective
when modified with lower-valent forms of sulfur (i.e., “sulfidated”).
Controlled sulfidation for this purpose (using sulfide, dithionite,
etc.) is the main topic of this review, but insights are derived by
comparison with related and comparatively well-characterized processes
such as corrosion of iron in sulfidic waters and abiotic natural attenuation
by iron sulfide minerals. Material characterization shows that varying
sulfidation protocols (e.g., concerted or sequential) and key operational
variables (e.g., S/Fe ratio and sulfidation duration) result in materials
with structures and morphologies ranging from core–shell to
multiphase. A meta-analysis of available kinetic data for dechlorination
under anoxic conditions, shows that sulfidation usually increases
dechlorination rates, and simultaneously hydrogen production is suppressed.
Therefore, sulfidation can greatly improve the efficiency of utilization
of reducing equivalents for contaminant removal. This benefit is most
likely due to inhibited corrosion as a result of sulfidation. Sulfidation
may also favor desirable pathways of contaminant removal, such as
(i) dechlorination by reductive elimination rather than hydrogenolysis
and (ii) sequestration of metals as sulfides that could be resistant
to reoxidation. Under oxic conditions, sulfidation is shown to enhance
heterogeneous catalytic oxidation of contaminants. These net effects
of sulfidation on contaminant removal by iron-based materials may
substantially improve their practical utility for water treatment
and remediation of contaminated groundwater