Next Article in Journal
Evaluation of Hemodialysis Arteriovenous Bruit by Deep Learning
Previous Article in Journal
The Various Oximetric Techniques Used for the Evaluation of Blood Oxygenation
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Letter

Evaluation of the Efficiency of Detection and Capture of Manganese in Aqueous Solutions of FeCeOx Nanocomposites Doped with Nb2O5

by
Artem Kozlovskiy
1,2,*,
Kamila Egizbek
1,2,
Maxim V. Zdorovets
1,2,3,
Milana Ibragimova
1,2,
Alena Shumskaya
4,
Alexandr A. Rogachev
4,
Zhanna V. Ignatovich
4 and
Kayrat Kadyrzhanov
1
1
Engineering Profile Laboratory, L.N.Gumilyov Eurasian National University, Satpaev str. 5, Nur-Sultan 010008, Kazakhstan
2
Laboratory of Solid State Physics, The Institute of Nuclear Physics, Ibrag and ov str. 1, Almaty 050032, Kazakhstan
3
Department of Intelligent Information Technologies, Ural Federal University, Mira str. 19, 620002 Ekaterinburg, Russia
4
Optical Anisotropic Films Laboratory, Institute of Chemistry of New Materials of the National Academy of Sciences of Belarus, 22007 Minsk, Belarus
*
Author to whom correspondence should be addressed.
Sensors 2020, 20(17), 4851; https://doi.org/10.3390/s20174851
Submission received: 2 August 2020 / Revised: 17 August 2020 / Accepted: 26 August 2020 / Published: 27 August 2020
(This article belongs to the Section Sensor Materials)

Abstract

:
The main purpose of this work is to study the effectiveness of using FeCeOx nanocomposites doped with Nb2O5 for the purification of aqueous solutions from manganese. X-ray diffraction, energy–dispersive analysis, scanning electron microscopy, vibrational magnetic spectroscopy, and mössbauer spectroscopy were used as research methods. It is shown that an increase in the dopant concentration leads to the transformation of the shape of nanoparticles from spherical to cubic and rhombic, followed by an increase in the size of the nanoparticles. The spherical shape of the nanoparticles is characteristic of a structure consisting of a mixture of two phases of hematite (Fe2O3) and cerium oxide CeO2. The cubic shape of nanoparticles is typical for spinel-type FeNbO4 structures, the phase contribution of which increases with increasing dopant concentration. It is shown that doping leads not only to a decrease in the concentration of manganese in model solutions, but also to an increase in the efficiency of adsorption from 11% to 75%.

1. Introduction

In recent years, special attention has been paid to nanocomposites based on metal oxides or ferrites, interest in which is due to the high potential for their use as catalysts, the basis for carriers of drugs, sensors and adsorbents of pollutants, and waste water treatment [1,2,3,4,5]. The wide range of their application is based on the possibility of obtaining nanostructured composites with large specific surface area, functional groups, and resistance to degradation [6,7]. Magnetic characteristics such as coercivity and saturation magnetization in turn allow the use of nanoparticles for purification of aqueous media by adsorption of contaminants on its surface and subsequent removal from solution by magnetic separation [8,9,10].
Among the variety of metal oxide nanocomposites and nanoparticles FeCeOx structures of the type have great potential in photocatalysis, biomedicine, purification of aqueous media, etc. [7,8,9,10,11,12]. Methods for preparing FeCeOx nanostructures are quite numerous, and in most of them multiphase amorphous-like structures are obtained, which makes their own adjustments for their application [13,14,15]. Additionally, the use of iron-containing nanoparticles or composites based on them is accompanied by a rapid rate of degradation of the crystal structure as a result of the oxidation of iron and its subsequent decay. One way to increase resistance to degradation, as well as changes in functional properties and surface is to dope nanocomposites FeCeOx various elements or compounds, which significantly increases their productivity, as well as structural and morphological properties [16,17,18,19,20].
Due to the aforesaid, the purpose of this work is consideration of a possibility of increase in efficiency of filtration and cleaning of water environments by means of nanocomposites of FeCeOx doped by oxide of niobium (Nb2O5). The choice as a dopant is Nb2O5 due to its wide use as a doping element of various composite materials in order to increase photocatalytic activity, due to the small width of the forbidden zone, good resistance to degradation, as well as the possibility of obtaining spinel stable phases [21,22,23,24,25]. The relevance of the study is to assess the potential use of nanocomposites for the purification of aqueous media from pollutants such as manganese, which is one of the harmful metals concentrated in wastewater. The possibility of adsorption of manganese on the surface of nanocomposites and their subsequent capture by magnets can be further used on a semi-industrial or industrial scale.

2. Experimental Part

The synthesis of nanocomposites was carried out in two stages, including the chemical deposition of FeCeOx (which is a mixture of two phases Fe2O3 and CeO2) [26] and subsequent mechanochemical mixing of amorphous-like FeCeOx nanoparticles with Nb2O5 nanoparticles in the set stoichiometric proportions and thermal annealing in the air atmosphere at a temperature of 1000 °C within 8 h.
The samples were cooled down together with a muffle furnace (Naberthetm, Bremen, Germany) for 24 h. The choice of the annealing temperature is due to phase transformations in FeCeOх nanoparticles with the formation of two stable phases Fe2O3 and CeO2. Earlier in [26], we examined in detail the phase transformations of FeCeOх nanoparticles as a result of thermal annealing in the temperature range from 400 to 800 °C, according to which, when the annealing temperature is increased above 600 °C, the structure of nanoparticles is a mixture of two phases Fe2O3 and CeO2. In this case, an increase in temperature leads to an increase in the degree of structural ordering and a decrease in distortions and deformations of the crystal lattice. However, experimental work with an increase in the annealing temperature above 1000 °C led to the formation of large agglomerates of micron-sized particles that are not suitable for research.
The study of changes in the shape and size of nanoparticles as a result of changes in the concentration of the dopant was carried out by analyzing images obtained using a scanning electron microscope TM3030 (Hitachi Ltd., Chiyoda, Tokyo, Japan). The study of the elemental composition and its change were carried out using the method of energy dispersive analysis performed on the attachment Bruker XFlash MIN SVE microanalysis system at voltage of 15 kV.
The phase composition and the dynamics of its change as a result of doping were determined on the basis of the obtained diffractograms recorded on a D8 Advance ECO powder diffractometer (Bruker), in the Bragg–Brentano geometry in the angle range 2θ = 20–80° with a step of 0.03°, radiation Cu-Kλ = 1.54 Å.
The determination of magnetic characteristics was carried out using the vibration magnetic spectroscopy method performed on the “Liquid Helium Free High Field Measurement System”, “Cryogenic LTD”.
The study of ultrafine magnetic parameters was carried out using the method of Mössbauer spectroscopy on the MS1104Em Mössbauer spectrometer (Ritverc, Chernogolovka, Russia) with a 57Co nuclei in the Rh matrix source. The calibration of the spectra obtained at room temperature was carried out using α-Fe absorber (Ritverc, Chernogolovka, Russia).
The study of the prospects of using the synthesized nanoparticles before and after doping as a basis for the purification of aqueous media from manganese by adsorption on the surface of nanoparticles and subsequent filtration was carried out using model aqueous solutions with a diluted manganese concentration of 22 mg/dm3. During the experiment, the solution was stirred to avoid the formation of a precipitate at the bottom of the beaker. Determination of the concentration of manganese before and after adsorption was carried out by determining the optical density in the wavelength range of 440–460 nm using the analyzer “Fluorat-02”. The concentration of nanoparticles was 0.001 g, the adsorption time was 5 h. After the end of the time, the nanoparticles were captured by the magnet and removed from the model medium.

3. Results and Discussion

Figure 1 shows images obtained using the method of scanning electron microscopy of synthesized nanoparticles before and after modification by doping. In the initial state, FeCeO3 nanoparticles are spherical particles, the average size of which, according to the distribution diagram (see Figure 2a), varies from 110–120 nm.
Doping of Nb2O5 with increasing concentration leads to changes not only in the size of nanoparticles, but also in the shape. A schematic representation of the resizing is shown in Figure 3.
Initially, spherical nanoparticles undergo transformation in several stages, depending on the concentration of the dopant. In the case when the concentration is 0.1–0.2 of the total mass of mixed nanoparticles, spherical nanoparticles first lose their shape due to fouling by growths and cubic or diamond-shaped inclusions, which is also reflected in changes in the size of nanoparticles (see Figure 2b,c) by the appearance of a second maximum in the region 60–70 nm. An increase in the concentration of the dopant to 0.3 leads to a complete transformation of nanoparticles from a spherical to a cubic or rhomboid shape, accompanied by an increase in the size of nanoparticles to 150–170 nm (see Figure 2d).
The Table 1 shows the elemental analysis data of the studied nanoparticles depending on the concentration of the dopant, as well as the specific surface area and the ratio of spherical and cubic nanoparticles.
As can be seen from the presented data, an increase in the concentration of the dopant Nb2O5 leads to the displacement of cerium atoms from the structure, while the iron content remains practically unchanged. Moreover, a change in the shape and size of nanoparticles leads to an increase in the specific surface area. However, for the case when the concentration of the dopant Nb2O5 was 0.3 of the total mass, which is characterized by the transformation of nanoparticles from a spherical to a cubic shape, a decrease in the specific surface area is observed. Furthermore, a change in the concentration of the dopant Nb2O5 leads to a change in the ratio of the types of particles with an almost complete predominance of the cubic and rhombic forms at a concentration of the dopant Nb2O5 of 0.3 of the total mass.
The assessment of the phase composition of the studied nanoparticles depending on the concentration of the dopant Nb2O5 is presented in Figure 4 (X-ray diffraction data) and Figure 5 (phase composition data). The general view of the diffraction patterns obtained using the shooting method in the Bragg–Brentano geometry indicates the polycrystallinity of the synthesized nanoparticles, as well as the presence of structural distortions arising in the process of grinding and subsequent thermal annealing.
The different shapes of diffraction reflections for the initial sample indicate the presence in the structure of two phases characteristic of hematite (Fe2O3) and cerium oxide CeO2, the phase ratio of which is approximately 1:2. In the case of doped nanoparticles, a change in the diffraction patterns is observed associated with the appearance of new additional peaks at 2θ = 24.2°, 25.7°, 28.1°, 30.2°, 31.8°, and 32.9°, characteristic of the monoclinic phase of FeNbO4-spinel type, whose contribution increases with increasing concentration dopant. In this case, the peaks characteristic of the Fe2O3 and CeO2 phases are also present in the diffractograms; however, their intensities decrease with an increase in the dopant concentration. The appearance of a new FeNbO4 phase in the structure of nanoparticles indicates a phase transformation that occurs during grinding and subsequent annealing. The diagrams of the phase ratios in the composition of nanoparticles presented in Figure 5 were obtained by full-profile analysis of X-ray diffractograms with the subsequent calculation of the contributions according to formula (1) [27]:
V admixture = R I phase I admixture + R I p h a s e ,
Iphase is the value of the integral intensity of the main phase, Iadmixture is the value of the integral intensities of impurity phases, the structure factor is R = 1.45.
According to the data presented in the diffraction patterns, an increase in the concentration of the dopant Nb2O5 leads to the displacement of the CeO2 phase from the structure of nanoparticles, as well as to the dominance of the FeNbO4 phase. In this case, a change in the phase composition leads to a change in the density of nanoparticles, the data of which are shown in Figure 6.
The magnetic characteristics of nanoparticles depending on the concentration of the dopant were studied using a vibrating magnetometer, hysteresis loops are shown in Figure 7, the results of calculating the magnetic characteristics are presented in Table 2.
In the initial state, nanoparticles have a significant coercivity value Hc = 200, Oe and small values of specific magnetic parameters Mr = 0.0375, emu/g, Ms = 0.26, emu/g.
The literature provides various values of magnetic parameters of the composite FeCeOx [27,28,29], which is associated with the particle size of iron oxide and its fraction in the composites. With sizes up to tens of nanometers, particles have superparamagnetic characteristics, with large sizes-ferromagnetic properties. The samples in question have an average size of 120 nm and have ferromagnetic properties, and low values of specific parameters are explained by the high content of non-magnetic phase in the composite.
When Nb2O5 is introduced into the reaction mixture and the FeNbO4 phase is formed in the structure of nanoparticles, there is a sharp change in the magnetic parameters, the connectivity increases 13 times for 0.9FeCeOx + 0.1Nb2O5 nanoparticles and 10 times for 0.8FeCeOx + 0.2Nb2O5 nanoparticles, the quadraticity of the hysteresis loops changes. The observed change is associated with surface magnetic effects occurring on FeCeOx particles, apparently, by the pinning of magnetic moments due to the formation of a new phase. However, a significant change in the phase composition in the 0.7FeCeOx + 0.3Nb2O5 nanoparticles sample and the formation of a new shape of structures leads to a weakening of the surface effects and a halving of the coercivity.
The estimation of the hyperfine magnetic parameters of the synthesized nanoparticles, as well as the effect of doping on the degree of magnetic disordering, was carried out by analyzing the Mössbauer spectra obtained at room temperature. The general view of the spectrum of nanoparticles in the initial state is characterized by the presence of two sextets of ultrafine magnetic fields of 515–516 kOe, which are characteristic of two types of ferromagnetic iron atoms (see Figure 8). The values of the hyperfine fields and also isomeric shifts for the initial nanoparticles are characteristic of structures such as hematite Fe2O3 with a partially disordered structure. Disordering and deviation of the hyperfine fields from the reference values of hematite is due to the presence of the CeO2 phase in the structure of nanoparticles. Additionally, the influence of the CeO2 phase on the degree of magnetic and structural ordering is evidenced by the ratio of the contributions of the partial spectra of two sextets 2.11:0.89, which is characteristic of the violation of stoichiometry at various levels of population in the A- and B-sublattices.
Figure 9 shows the data on the variation of the intensities of the contributions of the partial spectra depending on the concentration of the dopant Nb2O5, as well as the magnitude of the hyperfine magnetic fields in the A- and B- sublattices obtained from the analysis of the Mössbauer spectra.
For microparticles doped with Nb2O5 the emergence of a doublet and also decrease in the intensities of two sextets with the subsequent complete dominance of a doublet in the structure of the spectrum of 0.7FeCeOx + 0.3 Nb2O5 nanoparticles is observed. The appearance of a quadrupole paramagnetic doublet and the subsequent increase in its contribution is due to the doping effect and partial replacement of iron atoms with niobium with the subsequent formation of a spinel structure. At the same time, the decrease in the value of ultra-thin magnetic fields in the case of an increase in the concentration of dopant Nb2O5 may be due to the presence of a phase FeNbO4 in the structure, which is characterized by the spinel structure.
Figure 10 shows the data on changes in the cyclic current-voltage characteristics of the studied nanoparticles depending on the concentration of the dopant. For the initial nanoparticles, the nature of the change in the cyclic volt-amperogram has a nonlinear non-ohmic character, characterized by a region from 0.2 to 1.5 V with a sharp increase in conductivity, characteristic of the quadratic dependence of the change in current strength on the applied voltage, and subsequent smooth change in current strength depending on voltage. Furthermore, the presence of an abrupt behavior of a change in the current-voltage characteristic can be due to the presence of two phases in the structure, which create additional obstacles to the ballistic nature of charge transfer.
For doped nanoparticles, the character of the change in current-voltage characteristics is close to ohmic, without the obvious presence of regions with a quadratic dependence of the change in I on V. In this case, the formation of the FeNbO4 phase at low concentrations leads to a sharp increase in the resistivity of nanoparticles (see Figure 11). However, the dominance of the FeNbO4 phase, as well as transformation processes in the shape of nanoparticles, lead to structure ordering and a decrease in the resistance value.
Figure 12 shows the results of experiments on the purification of aqueous model solutions using synthesized nanoparticles from manganese by adsorption on the surface of nanoparticles and subsequent decrease in concentration in the model solution. An aqueous solution with a dissolved manganese concentration of 22 mg/dm3 was used as a model medium. The time of adsorption by placing 0.001 g of synthesized nanoparticles in a model solution was 5 h. After the end of the time, the nanoparticles were captured by the magnet and removed from the model medium.
According to the presented data, in the case of using the initial nanoparticles, the efficiency of reducing the concentration of manganese in the model solution after filtration was no more than 11%, while for doped nanoparticles, an increase in the concentration of the dopant leads to a sharp increase from 24% to 75% (see Figure 12b). An increase in the adsorption capacity of doped nanoparticles is due to a change in the morphological features of nanoparticles, as well as structural transformations, which more actively interact with the model solution and adsorb manganese on their surface, followed by its deposition on the surface of nanoparticles in the form of build-ups and small particles, which are clearly visible on SEM images nanoparticles after the filtration process (see Figure 13).
A direct confirmation of the fact that the formed small growths on the surface of nanoparticles are manganese are the data of the mapping results, which are presented in Figure 14, obtained from the 0.7FeCeOx + 0.3 Nb2O5 nanoparticles samples.
Figure 15a shows data on changes in the elemental content of manganese on the surface of nanoparticles, which was determined using the method of energy dispersive analysis. According to the data obtained, for the initial nanoparticles, the content of adsorbed manganese on the surface is no more than 4–5 at %, while for doped nanoparticles this value ranges from 7% to 12% depending on the concentration of the dopant.
An important feature of magnetic nanoparticles used for purification of aqueous media or photocatalytic decomposition reactions is the possibility of their complete extraction from solutions after filtration and a cycle of reactions using magnets. Figure 15b shows the data on the efficiency of trapping nanoparticles using magnets after 5 h of filtration, from which it can be seen that the percentage of trapping nanoparticles after filtration is 97–100% for modified nanoparticles, which indicates that the magnetic properties of nanoparticles are preserved after filtration. In this case, the degree of capture of 87% for the initial nanoparticles indicates a partial degradation of nanoparticles during the experiment. So, for example, in work [30] it was shown that after 24 h of staying in an aqueous solution of nanoparticles, their partial degradation is observed due to the formation of paramagnetic inclusions, which can reduce the collection efficiency. In this case, a long stay in the model solution leads to a decrease in the filtration efficiency due to the degradation of nanoparticles. However, in our case, the choice of a filtration time of five hours does not lead to any significant changes in the morphology of nanoparticles, as well as their degradation.

4. Conclusions

The paper demonstrates the efficiency of using FeCeOx doping of Nb2O5 nanoparticles in order not only to change the morphology and phase composition of nanoparticles, but also to increase the adsorption of manganese and increase the degree of purification. Resistance to degradation with an increase in the concentration of the dopant Nb2O5, as well as an increase in the purification efficiency, is due to the presence of a stable phase of the spinel type FeNbO4 in the structure. The high degree of capture efficiency for modified nanoparticles indicates the possibility of their reuse.
Further experiments will be aimed at studying the influence of various factors, such as the acidity of the medium, the concentration of nanoparticles in the model solution on the degree of purification.

Author Contributions

Conceptualization, A.K., M.V.Z., and K.K.; methodology, A.K., M.V.Z., and K.E.; formal analysis, A.S., M.V.Z., A.K., and M.I.; investigation, K.E., A.A.R., Z.V.I., and M.V.Z.; resources, K.K.; writing—original draft preparation, review and editing, A.K. and M.V.Z.; visualization, A.K.; supervision, M.V.Z.; project administration, M.V.Z.; and funding acquisition, K.K. and M.V.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Science Committee of the Ministry of Education and Science of the Republic of Kazakhstan (No. BR05235921).

Conflicts of Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

References

  1. Niu, L.; Wei, T.; Li, Q.; Zhang, G.; Xian, G.; Long, Z.; Ren, Z. Ce-based catalysts used in advanced oxidation processes for organic wastewater treatment: A review. J. Environ. Sci. 2020, 96, 109–116. [Google Scholar] [CrossRef]
  2. Zhang, Q.; Zhou, W.; Cui, Y.; Lyu, C.; Liu, T.; Zhang, R.; Zhang, R.; Zheng, J.; Shi, Z.; Lu, C.; et al. Iron triad nanomaterials and their sustainable application in the environment. Environ. Sci. Nano 2018, 5, 246–256. [Google Scholar] [CrossRef]
  3. Balcaen, V.; Poelman, H.; Poelman, D.; Marina, G.B. Kinetic modeling of the total oxidation of propane over Cu-and Ce-based catalysts. J. Catal. 2011, 283, 75–88. [Google Scholar] [CrossRef]
  4. Zhang, N.; Zhang, G.; Chong, S.; Zhao, H.; Huang, T.; Zhu, J. Ultrasonic impregnation of MnO2/CeO2 and its application in catalytic sono-degradation of methyl orange. J. Environ. Manag. 2017, 205, 134–141. [Google Scholar]
  5. Weia, X.; Zhuabcd, N.; Huanga, X.; Kanga, N.; Wuabcd, P.; Dangab, Z. Efficient degradation of sodium diclofenac via heterogeneous Fenton reaction boosted by Pd/Fe@Fe3O4 nanoparticles derived from bio-recovered palladium. J. Environ. Manag. 2020, 260, 110072. [Google Scholar] [CrossRef] [PubMed]
  6. Khataee, A.; Gholami, P.; Kalderis, D.; Pachatouridou, E.; Konsolakis, M. Preparation of novel CeO2-biochar nanocomposite for sonocatalytic degradation of a textile dye. Ultrason. Sonochem. 2018, 41, 503–513. [Google Scholar] [CrossRef] [PubMed]
  7. Chong, S.; Zhang, G.; Zhang, N.; Liu, Y.; Zhu, J.; Huang, T.; Fang, S. Preparation of FeCeO x by ultrasonic impregnation method for heterogeneous Fenton degradation of diclofenac. Ultrason. Sonochem. 2016, 32, 231–240. [Google Scholar] [CrossRef]
  8. Huang, F.; Wang, J.; Chen, W.; Wan, Y.; Wang, X.; Cai, N.; Liu, J.; Yu, F. Synergistic peroxidase-like activity of CeO 2 -coated hollow Fe 3 O 4 nanocomposites as an enzymatic mimic for low detection limit of glucose. J. Taiwan Inst. Chem. Eng. 2018, 83, 40–49. [Google Scholar] [CrossRef]
  9. Mura, S.; Jiang, Y.; Vassalini, I.; Gianoncelli, A.; Alessandri, I.; Granozzi, G.; Calvillo, L.; Senes, N.; Enzo, S.; Innocenzi, P.; et al. Graphene Oxide/Iron Oxide Nanocomposites for Water Remediation. ACS Appl. Nano Mater. 2018, 1, 6724–6732. [Google Scholar] [CrossRef]
  10. Kang, Y.-G.; Yoon, H.; Lee, C.-S.; Kim, E.-J.; Chang, Y.-S. Advanced oxidation and adsorptive bubble separation of dyes using MnO2-coated Fe3O4 nanocomposite. Water Res. 2019, 151, 413–422. [Google Scholar] [CrossRef]
  11. Wang, L.; Wang, J.; Liu, X.; Chen, Y.; Cheng, H.; Wu, Y.; Peng, H.; Mab, Z. FeCeOx with improved activity for catalytic reduction of NO with NH3. J. Phys. Chem. Solids 2020, 142, 109472. [Google Scholar] [CrossRef]
  12. Khataee, A.; Hassandoost, R.; Pouran, S.R. Cerium-substituted magnetite: Fabrication, characterization and sonocatalytic activity assessment. Ultrason. Sonochem. 2018, 41, 626–640. [Google Scholar] [CrossRef] [PubMed]
  13. Zhou, H.; Zhao, Z. The Preparation, Characterization and Photocatalytic Activity of FexCe1-xO2-n Microstructures. Integr. Ferroelectr. 2015, 164, 33–44. [Google Scholar] [CrossRef]
  14. Liu, J.; Zhou, J.; Ding, Z.; Zhao, Z.; Xu, X.; Fang, Z. Ultrasound irritation enhanced heterogeneous activation of peroxymonosulfate with Fe 3 O 4 for degradation of azo dye. Ultrason. Sonochem. 2017, 34, 953–959. [Google Scholar] [CrossRef]
  15. Channei, D.; Inceesungvorn, B.; Wetchakun, N.; Phanichphant, S.; Nakaruk, A.; Koshy, P.; Sorrell, C. Photocatalytic activity under visible light of Fe-doped CeO2 nanoparticles synthesized by flame spray pyrolysis. Ceram. Int. 2013, 39, 3129–3134. [Google Scholar] [CrossRef]
  16. Zhang, H.; Zhang, M.; Hao, L.; Wang, J.; Ma, Y.; Zhang, Y.; Jiao, T.; Zhang, W.; Chen, S.; Liang, P. Enhanced SO2 tolerance of FeCeOx/CNTs catalyst for NO and Hg0 removal by coating shell SiO2. Fuel Process. Technol. 2020, 201, 106342. [Google Scholar] [CrossRef]
  17. He, C.; Xu, B.-T.; Shi, J.-W.; Qiao, N.-L.; Hao, Z.; Zhao, J.-L. Catalytic destruction of chlorobenzene over mesoporous ACeOx (A=Co, Cu, Fe, Mn, or Zr) composites prepared by inorganic metal precursor spontaneous precipitation. Fuel Process. Technol. 2015, 130, 179–187. [Google Scholar] [CrossRef]
  18. Shafiee, M.R.M.; Sadeghian, M.; Kargar, M. ZnFe2O4-Fe2O3-CeO2 composite nanopowder: Preparation, magnetic properties, and 4-chlorophenol removal characterizations. Ceram. Int. 2017, 43, 14068–14073. [Google Scholar] [CrossRef]
  19. Ouyang, J.; Zhao, Z.; Subi, S.L.; Yang, H. Degradation of Congo Red dye by a Fe2O3@ CeO2-ZrO2/Palygorskite composite catalyst: Synergetic effects of Fe2O3. J. Colloid Interface Sci. 2018, 539, 135–145. [Google Scholar] [CrossRef]
  20. Shanmugam, V.; Sanjeevamuthu, S.; Jeyaperumal, K.S.; Vairamuthu, R. Construction of α-Fe2O3/CeO2 decorated g-C3N4 nanosheets for magnetically separable efficient photocatalytic performance under visible light exposure and bacterial disinfection. Appl. Surf. Sci. 2019, 488, 763–777. [Google Scholar]
  21. Liu, Y.; Szeifert, J.M.; Feckl, J.M.; Mandlmeier, B.; Rathousky, J.; Hayden, O.; Fattakhova-Rohlfing, D.; Bein, T. Niobium-Doped Titania Nanoparticles: Synthesis and Assembly into Mesoporous Films and Electrical Conductivity. ACS Nano 2010, 4, 5373–5381. [Google Scholar] [CrossRef] [PubMed]
  22. Kruefu, V.; Peterson, E.; Khantha, C.; Siriwong, C.; Phanichphant, S.; Carroll, D.L. Flame-made niobium doped zinc oxide nanoparticles in bulk heterojunction solar cells. Appl. Phys. Lett. 2010, 97, 53302. [Google Scholar] [CrossRef]
  23. Yue, J.; Suchomski, C.; Voepel, P.; Ellinghaus, R.; Rohnke, M.; Leichtweiss, T.; Elm, M.T.; Smarsly, B.M. Mesoporous niobium-doped titanium dioxide films from the assembly of crystalline nanoparticles: Study on the relationship between the band structure, conductivity and charge storage mechanism. J. Mater. Chem. A 2017, 5, 1978–1988. [Google Scholar] [CrossRef] [Green Version]
  24. Piggott, E.K.; Hope, T.O.; Crabbe, B.W.; Jalbert, P.-M.; Orlova, G.; Hallett-Tapley, G.L. Exploiting the photocatalytic activity of gold nanoparticle-functionalized niobium oxide perovskites in nitroarene reductions. Catal. Sci. Technol. 2017, 7, 5758–5765. [Google Scholar] [CrossRef]
  25. Zhang, C.; Ikeda, M.; Uchikoshi, T.; Li, J.-G.; Watanabe, T.; Ishigaki, T. High-concentration niobium (V) doping into TiO2 nanoparticles synthesized by thermal plasma processing. J. Mater. Res. 2011, 26, 658–671. [Google Scholar] [CrossRef]
  26. Kadyrzhanov, K.K.; Egizbek, K.; Kozlovskiy, A.L.; Zdorovets, M. Synthesis and Properties of Ferrite-Based Nanoparticles. Nanomaterials 2019, 9, 1079. [Google Scholar] [CrossRef] [Green Version]
  27. Gao, S.; Zhang, W.; Zhou, H.; Chen, D. Magnetic composite Fe3O4/CeO2 for adsorption of azo dye. J. Rare Earth 2018, 36, 986–993. [Google Scholar] [CrossRef]
  28. Channei, D.; Inceesungvorn, B.; Wetchakun, N.; Phanichphant, S. Synthesis of Fe3O4/SiO2/CeO2 core–shell magnetic and their application as photocatalyst. J. Nanosci. Nanotechnol. 2014, 14, 7756–7762. [Google Scholar] [CrossRef] [PubMed]
  29. Gan, G.; Liu, J.; Zhu, Z.; Yang, Z.; Zhang, C.; Hou, X. A novel magnetic nanoscaled Fe3O4/CeO2 composite prepared by oxidation-precipitation process and its application for degradation of orange G in aqueous solution as Fenton-like heterogeneous catalyst. Chemosphere 2017, 168, 254–263. [Google Scholar] [CrossRef]
  30. Egizbek, K.; Kozlovskiy, A.L.; Ludzik, K.; Zdorovets, M.V.; Ibragimova, M.A.; Marciniak, B.; Jazdzewska, M.; Chudoba, D.; Nazarova, A.; Kontek, R. Application of Fe2O3/CeO2 nanocomposites for the purification of aqueous media. Appl. Phys. A-Mater. 2020, 126, 477. [Google Scholar] [CrossRef]
Figure 1. SEM images of synthesized nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 1. SEM images of synthesized nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g001
Figure 2. Diagrams of nanoparticle size distribution depending on the dopant concentration: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx+ 0.3 Nb2O5 nanoparticles.
Figure 2. Diagrams of nanoparticle size distribution depending on the dopant concentration: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx+ 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g002
Figure 3. Schematic representation of the transformation of the geometry of the synthesized nanoparticles as a result of an increase in the concentration of the dopant Nb2O5.
Figure 3. Schematic representation of the transformation of the geometry of the synthesized nanoparticles as a result of an increase in the concentration of the dopant Nb2O5.
Sensors 20 04851 g003
Figure 4. X-ray diffraction pattern of the studied samples FeCeOx nanoparticles doped Nb2O5 with different concentration.
Figure 4. X-ray diffraction pattern of the studied samples FeCeOx nanoparticles doped Nb2O5 with different concentration.
Sensors 20 04851 g004
Figure 5. Phase analysis data obtained by analyzing X-ray diffractograms: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 5. Phase analysis data obtained by analyzing X-ray diffractograms: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g005
Figure 6. Graph of changes in the density of nanoparticles depending on the concentration of the dopant.
Figure 6. Graph of changes in the density of nanoparticles depending on the concentration of the dopant.
Sensors 20 04851 g006
Figure 7. Hysteresis loops of the studied nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 7. Hysteresis loops of the studied nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g007
Figure 8. Mössbauer spectra of nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 8. Mössbauer spectra of nanoparticles: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g008aSensors 20 04851 g008b
Figure 9. Changes in the hyperfine parameters of magnetic characteristics obtained on the basis of the analysis of Mössbauer data: (a) data of changes of contribution intensities of partial spectra depending on concentration of dopant Nb2O5; (b) data on changes in the magnitude of hyperfine magnetic fields in the A- and B- sublattices.
Figure 9. Changes in the hyperfine parameters of magnetic characteristics obtained on the basis of the analysis of Mössbauer data: (a) data of changes of contribution intensities of partial spectra depending on concentration of dopant Nb2O5; (b) data on changes in the magnitude of hyperfine magnetic fields in the A- and B- sublattices.
Sensors 20 04851 g009
Figure 10. Graphs of cyclic voltammograms of the studied nanoparticles: (a) FeCeOx nanoparticles; b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 10. Graphs of cyclic voltammograms of the studied nanoparticles: (a) FeCeOx nanoparticles; b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g010
Figure 11. Graph of change of resistance value depending on type of nanoparticles.
Figure 11. Graph of change of resistance value depending on type of nanoparticles.
Sensors 20 04851 g011
Figure 12. Results of filtration characteristics of aqueous solutions from nanoparticles: (a) diagram of manganese concentration change in model solutions after 5 h of filtration; (b) graph of efficiency of manganese filtration from model solutions.
Figure 12. Results of filtration characteristics of aqueous solutions from nanoparticles: (a) diagram of manganese concentration change in model solutions after 5 h of filtration; (b) graph of efficiency of manganese filtration from model solutions.
Sensors 20 04851 g012
Figure 13. SEM images of synthesized nanoparticles after separation: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Figure 13. SEM images of synthesized nanoparticles after separation: (a) FeCeOx nanoparticles; (b) 0.9FeCeOx + 0.1Nb2O5 nanoparticles; (c) 0.8FeCeOx + 0.2 Nb2O5 nanoparticles; and (d) 0.7FeCeOx + 0.3 Nb2O5 nanoparticles.
Sensors 20 04851 g013
Figure 14. Mapping results for 0.7FeCeOx + 0.3 Nb2O5 nanoparticles after filtration. (The color in the figure indicates the distribution of elements determined according to the mapping data: red—Fe, green—Ce, blue—Nb, orange—O, and yellow—Mn.)
Figure 14. Mapping results for 0.7FeCeOx + 0.3 Nb2O5 nanoparticles after filtration. (The color in the figure indicates the distribution of elements determined according to the mapping data: red—Fe, green—Ce, blue—Nb, orange—O, and yellow—Mn.)
Sensors 20 04851 g014aSensors 20 04851 g014b
Figure 15. Data of energy dispersion analysis and conservation of mass of nanoparticle samples after filtration: (a) graph of changes in the concentration of manganese on the surface of nanoparticles after filtration; (b) graph of the efficiency of capturing nanoparticles after filtration.
Figure 15. Data of energy dispersion analysis and conservation of mass of nanoparticle samples after filtration: (a) graph of changes in the concentration of manganese on the surface of nanoparticles after filtration; (b) graph of the efficiency of capturing nanoparticles after filtration.
Sensors 20 04851 g015
Table 1. Elemental analysis data, specific surface area, and particle type ratio.
Table 1. Elemental analysis data, specific surface area, and particle type ratio.
SampleFe, at.w.%Ce, at.w.%Nb, at.w.%O, at.w.%Specific Surface Area, m2/gRatio of Spherical and Cubic Nanoparticles
FeCeOx nanoparticles14.1 ± 1.129.5 ± 2.2-56.4 ± 3.40.0087100:0
0.9FeCeOx + 0.1Nb2O5 nanoparticles13.2 ± 1.522.2 ± 2.19.2 ± 1.255.4 ± 3.10.010978:22
0.8FeCeOx + 0.2 Nb2O5 nanoparticles13.6 ± 1.213.4 ± 1.314.1 ± 1.558.9 ± 2.50.012634:66
0.7FeCeOx + 0.3 Nb2O5 nanoparticles13.2 ± 1.37.8 ± 0.719.4 ± 1.259.6 ± 2.70.00983:97
Table 2. Magnetic characteristics data.
Table 2. Magnetic characteristics data.
SampleHc, Oe 1Mr, emu/g 2Ms, emu/g 3Mr/Ms 4
FeCeOx nanoparticles2000.03750.260.144
0.9FeCeOx + 0.1Nb2O5 nanoparticles25860.04480.1950.23
0.8FeCeOx + 0.2Nb2O5 nanoparticles20350.03950.3750.105
0.7FeCeOx + 0.3Nb2O5 nanoparticles9600.02070.1890.11
1 Hc, Oe—coercivity, 2 Mr, emu/g—remanent magnetization, 3 Ms, emu/g—saturation magnetization, 4 Mr/Ms—squareness.

Share and Cite

MDPI and ACS Style

Kozlovskiy, A.; Egizbek, K.; Zdorovets, M.V.; Ibragimova, M.; Shumskaya, A.; Rogachev, A.A.; Ignatovich, Z.V.; Kadyrzhanov, K. Evaluation of the Efficiency of Detection and Capture of Manganese in Aqueous Solutions of FeCeOx Nanocomposites Doped with Nb2O5. Sensors 2020, 20, 4851. https://doi.org/10.3390/s20174851

AMA Style

Kozlovskiy A, Egizbek K, Zdorovets MV, Ibragimova M, Shumskaya A, Rogachev AA, Ignatovich ZV, Kadyrzhanov K. Evaluation of the Efficiency of Detection and Capture of Manganese in Aqueous Solutions of FeCeOx Nanocomposites Doped with Nb2O5. Sensors. 2020; 20(17):4851. https://doi.org/10.3390/s20174851

Chicago/Turabian Style

Kozlovskiy, Artem, Kamila Egizbek, Maxim V. Zdorovets, Milana Ibragimova, Alena Shumskaya, Alexandr A. Rogachev, Zhanna V. Ignatovich, and Kayrat Kadyrzhanov. 2020. "Evaluation of the Efficiency of Detection and Capture of Manganese in Aqueous Solutions of FeCeOx Nanocomposites Doped with Nb2O5" Sensors 20, no. 17: 4851. https://doi.org/10.3390/s20174851

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop