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1 hetic magnetic nanoparticle (Co-doped Fe3O4 (magnetite)).
2 ntly converted to Fe(OH)2(s) intermixed with magnetite.
3 otic or biological origin of nanocrystals of magnetite.
4 uctures consistent with biogenically derived magnetite.
5 observed between the two humidity levels for magnetite.
6 olution in the presence of an excess of nano-magnetite.
7 hemite or maghemite layers at the surface of magnetite.
8 Fh) in an organic scaffold as a precursor to magnetite.
9 ossibly lost with formation of smectite plus magnetite.
10 e the three-dimensional structure of APBs in magnetite.
11 nged through coprecipitation with neo-formed magnetite.
12 30 min) and oxidation of Sn(II) to Sn(IV) by magnetite.
13 e adsorption and eventual incorporation into magnetite.
14 exists on NO3(-) and NO2(-) reactivity with magnetite.
15 an be directly immobilized on the surface of magnetite.
17 olvement of NO3(-) and nitrite (NO2(-)) with magnetite, a mixed valence Fe(2+)/Fe(3+) mineral found i
18 complexes with cosorbed Fe at the surface of magnetite, a possible consequence of the high concentrat
19 amples contaminated with PAHs and mixed with magnetite, a similar grinding-induced degradation patter
20 el papers based on epoxy nanocomposites with magnetite and carbon nanofiber (CNF) nanohybrids, withou
21 X-ray absorption spectroscopy indicate that magnetite and ferrihydrite formed in the column followin
22 acteristics of equidimensional cuboctahedral magnetite and find that, contrary to previously publishe
23 investigate the formation and persistence of magnetite and green rust (GR) NP phases produced via the
24 that secondary Fe(II)-bearing phases (e.g., magnetite and green rust), which commonly precipitate du
26 containing minerals, including hypersthene, magnetite and hematite, distributed in a light matrix of
28 on tests using ferrous ion in suspensions of magnetite and maghemite showed that surface-bound Fe(II)
29 sing a multistage column experiment in which magnetite and other minerals formed from added nitrate a
31 dicted geochemical variations indicates that magnetite and phyllosilicates formed by diagenesis under
32 thod is based on a nanocomposite composed of magnetite and silver nanoparticles, whose surface is mod
33 escribe the most common routes to synthesize magnetite and subsequently will introduce recent efforts
34 omplex with polymer nanoparticles containing magnetite and the T-cell growth factor interleukin-2 (IL
36 show that NAL was adsorbed at the surface of magnetite and was efficiently degraded under oxic condit
37 100 times less concentrated than in abiotic magnetite and we provide a quantitative pattern of this
38 first summarize the main characteristics of magnetite and what is known about the mechanisms of magn
39 g significant Fe and Mn (hematite, goethite, magnetite, and groutite) adsorbed Pu(V) faster than thos
40 of As(III)- and As(V)-doped lepidocrocite to magnetite, and to evaluate the influence of arsenic on t
42 ne ( approximately 3 wt.%), cation-deficient magnetite ( approximately 3 wt.%), cristobalite ( approx
43 bnormal elastic and vibrational behaviors of magnetite are attributed to the occurrence of the octahe
44 ions bound in the highly crystalline mineral magnetite are bioavailable as electron sinks and electro
45 ascribed to endogenous sources, these brain magnetites are often found with other transition metal n
48 Tc(VII) by reduction and incorporation into magnetite at high pH and with significant stability upon
52 h two metal oxides, TiO2 (rutile) and Fe3O4 (magnetite) (at <1.3 U nm(-2) and <0.037 U nm(-2), respec
55 esent a first step toward in vivo studies of magnetite biomineralization in magnetotactic bacteria.
56 one of the best model organisms for studying magnetite biomineralization, as their genomes are sequen
59 egulation of its activity is required during magnetite biosynthesis in vivo Our results represent the
61 igh oxygen fugacities, close to the hematite-magnetite buffer, that can contain significant amounts o
62 Here we explore the lithiation of nanosized magnetite by employing a strain-sensitive, bright-field
63 sphate, lepidocrocite was rapidly reduced to magnetite by Shewanella putrefaciens CN32, and over time
68 cs did not impact the redox chemistry of the magnetite-chromate system over the duration of the exper
70 to investigate the distribution behavior of magnetite coated carbon nanotubes (CNTs), which simplifi
71 plexation modeling, it was shown that the NA-magnetite complexation constant does not vary with Fe(II
75 reaction with glucose oxidase immobilized on magnetite covered with silica gel modified propylamine i
76 oute to achieve control over the kinetics of magnetite crystallization under ambient conditions and i
77 transported inside MTB for the production of magnetite crystals be spatially mapped using electron mi
79 predicted HtrA protease required to produce magnetite crystals in the magnetotactic bacterium Magnet
81 are magnetofossils, the fossilized chains of magnetite crystals produced by magnetotactic bacteria.
82 y magnetotactic bacteria (MTB) biomineralize magnetite crystals that nucleate and grow inside intrace
83 and magnetotactic bacteria are able to form magnetite crystals with well controlled sizes and shapes
94 (II) with a relevant redox-reactive mineral, magnetite (Fe(II)Fe(III)2O4) at <2 ppmv O2, and monitore
99 hat intracellular crystals of the iron oxide magnetite (Fe3O4) are coupled to mechanosensitive channe
100 g properties of the ferrimagnetic half metal magnetite (Fe3O4) are of continuing fundamental interest
105 , we explored the oxidative capacity of nano-magnetite (Fe3O4) having approximately 12 nm particle si
111 um Rhodopseudomonas palustris TIE-1 oxidizes magnetite (Fe3O4) nanoparticles using light energy.
112 show that supplementation of micrometer-size magnetite (Fe3O4) particles to a methanogenic sludge enh
115 interlocking dendritic crystals primarily of magnetite (Fe3O4), with wustite (FeO)+metal preserved in
118 This enhancement in binding capability of magnetite for NA is still observed in the presence of en
120 rkably resembles recent results on synthetic magnetite formation and bears a high similarity to sugge
121 of OM, OM reduced the amount of goethite and magnetite formation and increased the formation of lepid
122 ) mineral, followed by bioreduction and (bio)magnetite formation coupled to formation of a complex U(
123 s, MamE and MamO, during the early stages of magnetite formation in Magnetospirillum magneticum AMB-1
126 g goethite formation, reducing the amount of magnetite formation, and increasing the formation of a g
127 on was higher than As(III) removal following magnetite formation, which suggests that conversion of A
128 organisms use a twofold strategy to control magnetite formation: the mineral is formed from a poorly
131 understanding of the formation conditions of magnetite, GR, and ferric (oxyhydr)oxides in Fe EC, whic
132 ence that reduced iron (Fe) species, such as magnetite, green rust, and Fe sulfides, can also reduce
133 range of other minerals (hematite, goethite, magnetite, groutite, corundum, diaspore, and quartz) fou
134 2-) system was superior to the corresponding magnetite + H2O2 one in the presence of radical scavenge
136 ades intergrown among carbonate rosettes and magnetite-haematite granules, and is associated with car
138 f control over particle size and iron oxide (magnetite) homogeneity in chemical precipitation reactio
139 iquitous antiphase boundary (APB) defects in magnetite, however, direct information on their structur
143 ing of NO2(-) to positively charged sites on magnetite ( identical with S-OH2(+)) and to neutral site
144 ne the incorporation of 34 trace elements in magnetite in both cases of abiotic aqueous precipitation
145 es, or increased dissolution of fine-grained magnetite in forest soils due to increased soil moisture
148 ination of increased production of pedogenic magnetite in prairie soils, increased deposition of detr
149 irie soils, increased deposition of detrital magnetite in prairies from eolian processes, or increase
150 termediate is unresolvable from co-deposited magnetite in situ by other electrochemical techniques an
151 ) on formation and oxidative perturbation of magnetite in systems relevant to radioactive waste dispo
152 on the CIE clay, we suggest that most of the magnetite in the clay occurs as isolated, near-equidimen
154 w that phenol can be effectively degraded by magnetite in the presence of persulfate (S2O8(2-)) under
156 te and ferrous hydroxy carbonate, along with magnetite, in ferrihydrite systems, and siderite in hema
158 nto the magnetite structure and confirm that magnetite incorporated Tc(IV) is recalcitrant to oxidati
163 technetium migration under conditions where magnetite is formed including in geological disposal of
165 s reported in this study demonstrate that if magnetite is present in Fe(3+)-reducing soil and NO2(-)
166 ilization and dissolution of the passivating magnetite layer by reduction of structural Fe(III) coupl
168 c bacteria (MTB), the magnetic properties of magnetite magnetosomes have been extensively studied usi
172 ular machinery to construct linear chains of magnetite nanocrystals that allow the host cell to sense
175 gates with poly(acrylic acid)-functionalized magnetite nanoparticles (100 nm hydrodynamic diameter) a
176 bacteria Geobacter sulfurreducens, comparing magnetite nanoparticles (d approximately 12 nm) against
177 2, pH adjustment to 3.6, and the addition of magnetite nanoparticles (Fe3O4 MNPs) to the medium to pr
181 ork demonstrated the application of magnetic magnetite nanoparticles (MNPs) coated with a cationic po
183 gneticus sp. strain RS-1 forms bullet-shaped magnetite nanoparticles aligned along their (100) magnet
184 pitated, As(III) formed surface complexes on magnetite nanoparticles and As(V) is thought to have bee
190 cterially synthesized zinc- and cobalt-doped magnetite nanoparticles for biomedical applications.
191 olecularly imprinted polymer (MIP)-decorated magnetite nanoparticles for specific and label-free sulf
193 with approximately 90 and approximately 6 nm magnetite nanoparticles in the presence and absence of f
195 entify the abundant presence in the brain of magnetite nanoparticles that are consistent with high-te
196 del was developed for surface-functionalized magnetite nanoparticles that could simulate both the mea
197 eria synthesize highly uniform intracellular magnetite nanoparticles through the action of several ke
198 ed to synthesize polyvinylpyrrolidone-coated magnetite nanoparticles to separate a reference MC252 oi
199 a perform biomineralization of intracellular magnetite nanoparticles under a controlled pathway.
201 tion of 3-aminopropyltrimethoxysilane coated magnetite nanoparticles with antibody (antiHER2/APTMS-Fe
206 markably, these highly organized crystalline magnetite nanostructures directly bound into fibrillar A
208 Ferrihydrite (NAu1), lepidocrocite, and magnetite (NAu2) were detected as secondary mineralizati
214 at the electrochemical reduction of U(VI) on magnetite only yields U(V), even at a potential of -0.9
215 rated with linkers/ligands on the surface of magnetite or alternatively the organocatalysts can be di
216 ze ordered chains of uniform, membrane-bound magnetite or greigite nanocrystals that exhibit nearly p
217 t usually takes place only in single crystal magnetite or thick epitaxial films at low temperatures.
218 alts and oxides and possibly the crystalline magnetite (otherwise detrital) are primary precipitates
220 iswaldense, a model MTB with equidimensional magnetite particles aligned along their (111) magnetic e
222 n transmission electron microscopy of the Ti-magnetite particles provides no evidence of NpO2 nanopar
223 erspecies electron transfer (DIET), based on magnetite particles serving as electron conduits between
224 cies are only observed for the more oxidized magnetite particles that contain lower Fe(II) content (x
225 rcivity, non-interacting, single-domain (SD) magnetite particles, whereas the South China Sea samples
230 associated exclusively with green rust, When magnetite precipitated, As(III) formed surface complexes
233 As(III) to As(V) is preferred when using As-magnetite precipitation to treat As-contaminated groundw
234 ontium and calcium incorporation to identify magnetite produced by magnetotactic bacteria in the geol
236 ings support climate as a primary control on magnetite production in soils, while demonstrating how c
239 within the low temperature superstructure of magnetite provides new insights into the charge and trim
240 ugite, and pigeonite, with minor K-feldspar, magnetite, quartz, anhydrite, hematite, and ilmenite.
242 uating/localized electronic order was shown, magnetite represents a model system for understanding co
243 strate reveals that the electrodeposition of magnetite requires the preceding adsorption of Fe(II)-tr
246 ive oxygen adsorption, occurs uniformly over magnetite's terraces, not preferentially at its surface
248 controlled conditions, cubic nanocrystals of magnetite self-assemble into arrays of helical superstru
250 resolved, laser-induced particles of natural magnetite, siderite, pyrrhotite, and pyrite, collected t
253 Bulk oxidation state analysis of the final magnetite solid phase by XANES shows that the majority o
254 Hg(II) to Hg(0) is observed over a range of magnetite stoichiometries (0.29 < x < 0.50) in purged he
258 ved for nitroaromatic compounds and uranium, magnetite stoichiometry appears to influence the rate of
259 confirming that it is important to consider magnetite stoichiometry when assessing the fate of conta
260 or significant Tc(IV) incorporation into the magnetite structure and confirm that magnetite incorpora
264 % with a conversion of 90-96% using the nano-magnetite supported aminomethylphosphine-Pd(II) complexe
265 tion of nanosize uranium precipitates on the magnetite surface at reducing potentials and dissolution
267 ween octahedrally coordinated Sn(IV) and the magnetite surface, indicative of formation of tetradenta
272 creased for goethite and hematite, while for magnetite, the relative solubility was similar for all o
273 pH-dependence in the reduction of NO2(-) by magnetite; the initial rate of NO2(-) removal was two ti
274 does not disproportionate but stabilizes on magnetite through precipitation of mixed-valence state U
275 y examining the oxidation of Fe(3-x)Ti(x)O4 (magnetite-titanomagnetite) nanoparticles by the bacteria
277 has potential implications on the ability of magnetite to be used for long range electron transport i
278 oichiometry strongly affects the capacity of magnetite to bind not only quinolone antibiotics such as
279 NES and EXAFS) showed a partial oxidation of magnetite to maghemite during the reaction, and four byp
280 olution despite significant oxidation of the magnetite to maghemite/goethite: All solid associated Tc
281 the decrease in MS is the transformation of magnetite to siderite, coupled with the exhaustion of fe
282 ribution as a function of composition in the magnetite-ulvospinel solid solution, important uncertain
283 vestigates NO3(-) and NO2(-) reactivity with magnetite under anoxic conditions using batch kinetic ex
285 We have studied a highly stoichiometric magnetite using inelastic X-ray scattering, X-ray diffra
289 cipitation with or adsorption onto preformed magnetite was investigated by X-ray diffraction (XRD), s
291 wanella putrefaciens CN32, and over time the magnetite was partially transformed to ferrous hydroxy c
292 ical properties, the chemical composition of magnetite was proposed as a promising tracer for bacteri
294 oparticles of the strongly magnetic mineral, magnetite, were first detected in the human brain over 2
295 r, in contrast to previous studies with pure magnetite where U(VI) was reduced to nanocrystalline ura
298 ere, we evaluated the reduction of Hg(II) by magnetites with varying Fe(II) content in both the absen
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