Next Article in Journal
Molecular Dynamics Simulation of the Influence of Nanoscale Structure on Water Wetting and Condensation
Previous Article in Journal
Nozzle-Shaped Electrode Configuration for Dielectrophoretic 3D-Focusing of Microparticles
Previous Article in Special Issue
A Novel Bismuth-Chitosan Nanocomposite Sensor for Simultaneous Detection of Pb(II), Cd(II) and Zn(II) in Wastewater

Micromachines 2019, 10(9), 586;

Fabrication of MoO3 Nanowire-Based Membrane Devices for the Selective Adsorption of Cationic Dyes from Aqueous Solutions with High Performance and Reusability
Department of Chemistry and Chemical Engineering, Inha University, 100 Inharo, Incheon 22212, Korea
Author to whom correspondence should be addressed.
Received: 23 July 2019 / Accepted: 30 August 2019 / Published: 31 August 2019


A series of ultralong (up to tens of micrometers) MoO3 nanowire-based membranes were synthesized for the treatment of aqueous solutions containing the cationic dyes methylene blue (MB) and rhodamine B (RhB). This treatment method possesses extremely rapid and superhigh adsorbability (up to 521 and 321 mg/g for MB and RhB, respectively), as well excellent selective adsorption ability of cationic dyes with respect to the anionic dye methyl orange (MO). Moreover, the cationic dyes on the membrane can be desorbed easily, and reusability is good.
MoO3; nanowires; cationic dyes; repeatability

1. Introduction

Recently, water contamination by dyes has been attracting much attention. Among the contaminating dyes, cationic dyes, such as methylene blue (MB) and rhodamine B (RhB), are widely used in dying cotton, printing, and dying textiles [1,2,3]. Although MB and RhB are not regarded as very toxic dyes, they also can produce some harmful effects to human health. Consequently, industrial effluent containing MB and RhB has to be treated before discharge. Recently, various methods have been developed to solve this issue, such as photocatalytic degradation, flocculation–coagulation, precipitation, and filtration [4,5,6,7,8,9,10]. Comparatively speaking, membrane filtration has received more attention because of its low cost, high efficiency, and flexible design. To date, although many nanomaterials including activated carbon, carbon nanotube, and graphene [11,12,13] have been explored to remove dyes from wastewater, there are still some disadvantages in their use that need to be overcome, such as high cost, unrecyclability, and possible secondary pollution [14,15,16,17,18]. Therefore, it is necessary to develop desirable materials that not only can adsorb dyes with high efficiency but also can be reused with good recyclability. Molybdenum oxide (MoO3), a prominent material among metal oxides, has been regarded as a suitable choice owing to its chemical stability, nontoxicity, high adsorbability, and low price [19,20,21,22,23]. Up till now, MoO3 has been used in various applications including photocatalysis, supercapacitors, photovoltaics, batteries, and electrocatalysis [24,25,26,27]. However, research about dye adsorption by MoO3 nanowire-based membranes is still limited. With this in mind, we designed and synthesized a type of MoO3 nanowire-based membrane to investigate its adsorption properties and recyclability behavior for dye removal.

2. Experimental Section

In this research, we synthesized a novel MoO3 nanowire-based membrane at various thicknesses. The MoO3 nanowires could be prepared by a hydrothermal method. The procedure is explained in detail in the Electronic Supporting Information. This kind of nanowire could easily be assembled into a flexible film by a vacuum and pressing procedure. This MoO3 nanowire-based membrane exhibited a superhigh adsorbability, as well as excellent selective adsorption of cationic dyes (Figure 2 and Figure 3).

3. Results and Discussion

The surface morphology of the as-synthesized nanowires is shown in Figure 1a,b. All the as-prepared samples showed the presence of wire-like MoO3 with a diameter of 200−400 nm and a length of 80–100 µm. Besides, the transmission electron microscope (TEM) observations and the phase information were confirmed by selected-area electron diffraction (SAED), as displayed in Figure 1c and d. The SAED patterns exhibited disparate diffraction spots, revealing the hybrid characteristics of MoO3. Meanwhile, X-ray diffraction (XRD) was also used to clarify the phase purities and crystal structures of the as-synthesized samples. The diffraction peaks at 12.6°, 25.4°, and 38.8° could be indexed to the (020), (040), and (060) planes of MoO3 (PDF No. 05-0508) in Figure 1e, respectively, which indicated high phase purity [28,29,30]. As mentioned above, the as-prepared membrane was composed of nanowires with a diameter of 400 nm and a length of hundreds of micrometers. We found that it was extremely stable in aqueous solution without sediment even after one day (Figure S1). As we know, after the vacuum-driven process, a large number of pores with various diameters form and are effective for molecular filtration.
The separation performance of the membrane (5 μm) for different dyes is shown in Figure 2. The UV–vis spectra of the aqueous dye solution (10 ppm) before and after filtration are displayed in Figure 2a–c. It is clear that after vacuum filtration, MB and RhB were totally removed (see also Movie S1 and Movie S2 in the Supporting Information). Meanwhile, only 24.6% of MO was removed under the same conditions, which is in agreement with the phenomenon shown in Movie S3. The FT-IR spectra of the adsorbed and desorbed membranes are displayed in Figure 2e,f, in which more peaks appear between 1200 and 1700 cm−1, which can be ascribed to the adsorbed dyes on the surface. After desorbing, the peaks between 1200 and 1700 cm−1 disappeared. This confirmed that the dyes could be adsorbed and desorbed easily in the presence of MoO3 nanowires. The membranes after filtration are shown in Figure S2. The front and back sides of the membranes indicate that there were no MB and RhB on the back side, which is in agreement with Figure 2. Moreover, we obtained the same results when increasing the ppm level (Figure 2d). In addition, the permeation performance of membranes with different thicknesses and various pH values was evaluated by examining the dye aqueous solution fluxes through the membranes. As presented in Figure S3a, the flux curve was consistent with the Hagen–Poiseuille theoretical models (Equation (1)) [31].
Δ P = 8 μ L Q π R 4
where ΔP is the pressure difference between the two ends, L is the length of pipe, μ is the dynamic viscosity, Q is the volumetric flow rate, and R is the pipe radius.
The water flux of the 5 μm membrane was 3782 L·h−1·m−2·bar−1, which is higher than that of traditional commercial filtration membranes (Figure S3a). The dramatically enhanced permeation performance is believed to be due to the pores in the membrane, which provide unobstructed channels for the water to pass, and to the ultrathin membrane thickness, which offers a low friction resistance. We also measured the separation performance at various pH values (Figure S3b), MB solutions at various pH values were prepared using 1 mol/L of HCl or NaOH. The results indicate that the as-prepared membranes had excellent pH tolerance and, therefore, an excellent application prospect.
We further investigated the selective adsorption performance of the membrane during filtration. Dye mixtures of MB +MO, RhB + MO, MB + RhB were prepared (10 ppm). For comparison, the UV–vis spectra of dye mixtures were measured, and the spectra are shown in Figure 3a–c (black lines). We also collected the filtered solutions, whose spectra are also displayed in Figure 3a,b (red lines). As shown in Movie S4 (MB + MO) and Movie S5 (RhB + MO), when the dye mixture aqueous solution was filtered through the MoO3 membrane, the filtered solution turned orange for MB + MO and RhB + MO. Regarding the mixture MB + RhB, the solution became transparent. These results proved the selective adsorption performance for MB and RhB. The adsorption capacity is another crucial parameter for practical applications. Figure 3d shows adsorption capacities of 512 mg/g (MB), 321 mg/g (RhB), and 25 mg/g (MO). The adsorption capacities of MB and RhB were almost 20 and 13 times higher than that for MO), which is in agreement with the basic theory underlying the selective adsorption performance for cationic dyes. Furthermore, the adsorption capacity of the membrane was much higher than that of commercial filtration adsorbents (Table S1), such as activated carbon, transition metal oxides, and other biomass-derived carbon adsorbents [32,33,34]. The process of selective adsorption of cationic dyes is shown in Scheme 1.
Apart from the fast adsorption rate and high adsorption capacity, a high reusability is equally important for a good adsorbent. In our study, we also conducted a reusability test under the same conditions. The regeneration process of the MoO3 nanowire-based membrane is displayed in the Supporting Information. As described, the used MoO3 nanowire-based membrane (0.5 g) was redispersed in ultrapure water by sonication and then activated with a dilute solution of NaCl (100 mL, 2 mol/L) and dimethylformamide (DMF) (50 mL) under sonication at room temperature to remove the adsorbed MB, RhB, or MO. The re-generated MoO3 nanowires were washed with water and ethanol several times until they became neutral and reused for the next adsorption experiment. For the reusability study, 0.5 g of as-prepared MoO3 nanowires were re-dispersed into 100 mL of deionized water and sonicated for 30 min to form a milky suspension. Then, the suspension was slowly transferred onto a membrane filter (Polytetrafluoroethylene, 0.45 μm) under a vacuum pressure of 0.1 MPa. After drying and peeling off the supporting substrate, the MoO3 nanowire-based membrane was ready to be reused in the same process. The same procedure was conducted four times, and the results were shown in Figure 4. After each recycling step, the regenerated MoO3 nanowires were added into the dye aqueous solutions (10 ppm). It is obvious that the adsorbent was still able to remove more than 90% of each dye after four cycles. Furthermore, it is known that the wettability of materials is a crucial factor affecting their filtrating performance. As shown in Figure S4, the contact angle of the membrane was 111.48, and that of MoO3 is 34.12 degree. Therefore, the MoO3 nanowire-based membrane is hydrophilic, and this characteristic facilitates water transfer among materials during the filtration process. These inherent characteristics are of great value for practical use. Meanwhile, we also try to compare the adsorption ability with those of other adsorbents reported in the literature. Detailed information is shown in Table 1.

4. Conclusions

In conclusion, we have developed a facile method to synthesize a MoO3 nanowire-based membrane, which was used for the selective adsorption of cationic dyes from aqueous solutions of mixed dyes. The adsorption rate and adsorption capacities of the new membrane are higher than those of traditional commercial membranes. Notably, the recyclability of this material is outstanding, as its adsorption ability is maintained after four cycles. Moreover, a limited loss of performance during the recycling procedure can reduce the costs, and suggests a bright future for the practical application of this system. Lastly, we hope this system can be of inspiration for the design of similar materials for the selective separation of other organics with low molecular weight.

Supplementary Materials

The following are available online at, Figure S1: (a) As prepared MoO3 nanowires sonicated for 30 min in the water; (b) Standing for one day, Figure S2: Front side and back side of as-synthesized MoO3 nanowires membrane after filtrating with various dyes, Figure S3: (a) Variation of MB solution flux with different membrane thickness; (b) Adsorption percentage of 5 μm membrane under different pH, Figure S4: Contact angle tendency of as-prepared MoO3 nanowires based membrane (34.12°), Table S1: Comparison of MB adsorption capacity of the as prepared MoO3 nanowires with other reported adsorbents, Video S1: Methylene blue (MB), Video S2: Rhodamine B (RhB), Video S3: Methyl orange (MO), Video S4: Methylene blue (MB) + Methyl orange (MO), Video S5: Rhodamine B (RhB) + Methyl orange (MO).

Author Contributions

Conceptualization, Y.Z. and S.-J.P.; methodology, Y.Z. and S.-J.P.; validation, Y.Z. and S.-J.P.; data curation, Y.Z. and S.-J.P.; writing-original draft, Y.Z. and S.-J.P.; visualization, Y.Z. and S.-J.P.; supervision, S.-J.P.; project administration, S.-J.P.; funding acquisition, S.-J.P.


This research was supported by Korea Evaluation institute of Industrial Technology (KEIT) through the Carbon Cluster Construction project (10083586, Development of petroleum based graphite fibers with ultra-high thermal conductivity) funded by the Ministry of Trade, Industry and Energy (MOTIE, Korea) and the Commercialization Promotion Agency for R and D Outcomes (COMPA) funded by the Ministry of Science and ICT(MSIT) (2018_RND_002_0064, Development of 800 mA h/g pitch carbon coating materials).

Conflicts of Interest

The authors declare no conflict of interest.


  1. Borthakur, P.; Das, M.R. Hydrothermal assisted decoration of NiS2 and CoS nanoparticles on the reduced graphene oxide nanosheets for sunlight driven photocatalytic degradation of azo dye: Effect of background electrolyte and surface charge. J. Colloid Interface Sci. 2018, 516, 342–354. [Google Scholar] [CrossRef]
  2. Ezugwu, C.I.; Asraf, M.A.; Li, X.; Liu, S.; Kao, C.M.; Zhuiykov, S.; Verpoort, F. Selective and adsorptive removal of anionic dyes and CO2 with azolium-based metal-organic frameworks. J. Colloid Interface Sci. 2018, 519, 214–223. [Google Scholar] [CrossRef]
  3. Yang, S.; Xu, C.Y.; Zhang, B.Y.; Yang, L.; Hu, S.P.; Zhen, L. Ca(II) doped beta-In2S3 hierarchical structures for photocatalytic hydrogen generation and organic dye degradation under visible light irradiation. J. Colloid Interface Sci. 2017, 491, 230–237. [Google Scholar] [CrossRef]
  4. He, Y.-C.; Yang, J.; Kan, W.-Q.; Zhang, H.-M.; Liu, Y.-Y.; Ma, J.-F. A new microporous anionic metal–organic framework as a platform for highly selective adsorption and separation of organic dyes. J. Mater. Chem. A 2015, 3, 1675–1681. [Google Scholar] [CrossRef]
  5. Zhang, Y.; Park, M.; Kim, H.-Y.; El-Newehy, M.; Rhee, K.Y.; Park, S.-J. Effect of TiO2 on photocatalytic activity of polyvinylpyrrolidone fabricated via electrospinning. Composites Part B 2015, 80, 355–360. [Google Scholar] [CrossRef]
  6. Wu, G.; Zhao, Y.; Li, Y.; Ma, H.; Zhao, J. pH-dependent synthesis of iodine-deficient bismuth oxyiodide microstructures: Visible-light photocatalytic activity. J. Colloid Interface Sci. 2018, 510, 228–236. [Google Scholar] [CrossRef]
  7. Park, S.J.; Kim, B.J. Ammonia removal of activated carbon fibers produced by oxyfluorination. J. Colloid Interface Sci. 2005, 291, 597–599. [Google Scholar] [CrossRef]
  8. Liu, T.; Li, B.; Hao, Y.; Yao, Z. MoO3-nanowire membrane and Bi2Mo3O12/MoO3 nano-heterostructural photocatalyst for wastewater treatment. Chem. Eng. J. 2014, 244, 382–390. [Google Scholar] [CrossRef]
  9. Yu, L.; Ruan, S.; Xu, X.; Zou, R.; Hu, J. One-dimensional nanomaterial-assembled macroscopic membranes for water treatment. Nano Today 2017, 17, 79–95. [Google Scholar] [CrossRef]
  10. Xu, Y.; Yuan, D.; Bao, J.; Xie, Y.; He, M.; Shi, Z.; Chen, S.; He, C.; Zhao, W.; Zhao, C. Nanofibrous membranes with surface migration of functional groups for ultrafast wastewater remediation. J. Mater. Chem. A 2018, 6, 13359–13372. [Google Scholar] [CrossRef]
  11. Zhang, Y.; Park, S.-J. Incorporation of RuO2 into charcoal-derived carbon with controllable microporosity by CO2 activation for high-performance supercapacitor. Carbon 2017, 122, 287–297. [Google Scholar] [CrossRef]
  12. Li, B.; Jiang, X.; Yin, J. Multi-responsive microgel of hyperbranched poly(ether amine) (hPEA-mGel) for the selective adsorption and separation of hydrophilic fluorescein dyes. J. Mater. Chem. 2012, 22, 17976. [Google Scholar] [CrossRef]
  13. Park, S.-J.; Seo, M.-K.; Lee, Y.-S. Surface characteristics of fluorine-modified PAN-based carbon fibers. Carbon 2003, 41, 723–730. [Google Scholar] [CrossRef]
  14. Xie, S.; Zheng, B.; Kuang, Q.; Wang, X.; Xie, Z.; Zheng, L. Synthesis of layered protonated titanate hierarchical microspheres with extremely large surface area for selective adsorption of organic dyes. CrystEngComm 2012, 14, 7715. [Google Scholar] [CrossRef]
  15. Zhang, Y.; Park, S.-J. Au–pd bimetallic alloy nanoparticle-decorated BiPO4 nanorods for enhanced photocatalytic oxidation of trichloroethylene. J. Catal. 2017, 355, 1–10. [Google Scholar] [CrossRef]
  16. Zhu, Z.; Bai, Y.L.; Zhang, L.; Sun, D.; Fang, J.; Zhu, S. Two nanocage anionic metal-organic frameworks with rht topology and {[M(H2O)6]6}12+ charge aggregation for rapid and selective adsorption of cationic dyes. Chem. Commu. 2014, 50, 14674–14677. [Google Scholar] [CrossRef]
  17. Deng, S.; Wang, R.; Xu, H.; Jiang, X.; Yin, J. Hybrid hydrogels of hyperbranched poly(ether amine)s (hPEAs) for selective adsorption of guest molecules and separation of dyes. J. Mater. Chem. 2012, 22, 10055. [Google Scholar] [CrossRef]
  18. Deng, S.; Xu, H.; Jiang, X.; Yin, J. Poly(vinyl alcohol) (PVA)-Enhanced Hybrid Hydrogels of Hyperbranched Poly(ether amine) (hPEA) for Selective Adsorption and Separation of Dyes. Macromolecules 2013, 46, 2399–2406. [Google Scholar] [CrossRef]
  19. Li, H.-H.; Li, Z.-Y.; Wu, X.-L.; Zhang, L.-L.; Fan, C.-Y.; Wang, H.-F.; Li, X.-Y.; Wang, K.; Sun, H.-Z.; Zhang, J.-P. Shale-like Co3O4 for high performance lithium/sodium ion batteries. J. Mater. Chem. A 2016, 4, 8242–8248. [Google Scholar] [CrossRef]
  20. Hassan, M.F.; Guo, Z.P.; Chen, Z.; Liu, H.K. Carbon-coated MoO3 nanobelts as anode materials for lithium-ion batteries. J. Power Sources 2010, 195, 2372–2376. [Google Scholar] [CrossRef]
  21. Wang, C.; Wu, L.; Wang, H.; Zuo, W.; Li, Y.; Liu, J. Fabrication and Shell Optimization of Synergistic TiO2-MoO3 Core-Shell Nanowire Array Anode for High Energy and Power Density Lithium-Ion Batteries. Adv. Funct. Mater. 2015, 25, 3524–3533. [Google Scholar] [CrossRef]
  22. Wang, G.; Ni, J.; Wang, H.; Gao, L. High-performance CNT-wired MoO3 nanobelts for Li-storage application. J. Mater. Chem. A 2013, 1, 4112. [Google Scholar] [CrossRef]
  23. Zhang, J.; Yu, A. Nanostructured transition metal oxides as advanced anodes for lithium-ion batteries. Sci. Bull. 2015, 60, 823–838. [Google Scholar] [CrossRef]
  24. Mai, L.; Yang, F.; Zhao, Y.; Xu, X.; Xu, L.; Hu, B.; Luo, Y.; Liu, H. Molybdenum oxide nanowires: Synthesis & properties. Mater. Today 2011, 14, 346–353. [Google Scholar]
  25. Chernova, N.A.; Roppolo, M.; Dillon, A.C.; Whittingham, M.S. Layered vanadium and molybdenum oxides: Batteries and electrochromics. J. Mater. Chem. 2009, 19, 2526. [Google Scholar] [CrossRef]
  26. Lou, S.N.; Ng, Y.H.; Ng, C.; Scott, J.; Amal, R. Harvesting, storing and utilising solar energy using MoO3: Modulating structural distortion through pH adjustment. ChemSusChem 2014, 7, 1934–1941. [Google Scholar] [CrossRef]
  27. Lou, S.N.; Yap, N.; Scott, J.; Amal, R.; Ng, Y.H. Influence of MoO3 (110) crystalline plane on its self-charging photoelectrochemical properties. Sci. Rep. 2014, 4, 7428. [Google Scholar] [CrossRef]
  28. Riley, L.A.; Lee, S.-H.; Gedvilias, L.; Dillon, A.C. Optimization of MoO3 nanoparticles as negative-electrode material in high-energy lithium ion batteries. J. Power Sources 2010, 195, 588–592. [Google Scholar] [CrossRef]
  29. Tsumura, T.; Inagaki, M. Lithium insertion/extraction reaction on crystalline MoO3. Solid State Ionics 1997, 104, 183–189. [Google Scholar] [CrossRef]
  30. Madhu Mohan, V.; Bin, H.; Chen, W. Enhancement of electrochemical properties of MoO3 nanobelts electrode using PEG as surfactant for lithium battery. J. Solid State Electrochem. 2010, 14, 1769–1775. [Google Scholar] [CrossRef]
  31. Chen, T.; Duan, M.; Shi, P.; Fang, S. Ultrathin nanoporous membranes derived from protein-based nanospheres for high-performance smart molecular filtration. J. Mater. Chem. A 2017, 5, 20208–20216. [Google Scholar] [CrossRef]
  32. Ghosal, A.; Shah, J.; Kotnala, R.K.; Ahmad, S. Facile green synthesis of nickel nanostructures using natural polyol and morphology dependent dye adsorption properties. J. Mater. Chem. A 2013, 1, 12868. [Google Scholar] [CrossRef]
  33. Li, J.; Huang, Y.; Liu, Z.; Zhang, J.; Liu, X.; Luo, H.; Ma, Y.; Xu, X.; Lu, Y.; Lin, J.; et al. Chemical activation of boron nitride fibers for improved cationic dye removal performance. J. Mater. Chem. A 2015, 3, 8185–8193. [Google Scholar] [CrossRef]
  34. Shen, Y. Carbothermal synthesis of metal-functionalized nanostructures for energy and environmental applications. J. Mater. Chem. A 2015, 3, 13114–13188. [Google Scholar] [CrossRef]
  35. Yener, J.; Kopac, T.; Dogu, G.; Dogu, T. Dynamic analysis of sorption of Methylene Blue dye on granular and powdered activated carbon. Chem. Eng. J. 2008, 144, 400–406. [Google Scholar] [CrossRef]
  36. Liu, T.; Li, Y.; Du, Q.; Sun, J.; Jiao, Y.; Yang, G.; Wang, Z.; Xia, Y.; Zhang, W.; Wang, K.; et al. Adsorption of methylene blue from aqueous solution by graphene. Colloids Surf. B 2012, 90, 197–203. [Google Scholar] [CrossRef]
  37. Li, Y.; Du, Q.; Liu, T.; Peng, X.; Wang, J.; Sun, J.; Wang, Y.; Wu, S.; Wang, Z.; Xia, Y.; et al. Comparative study of methylene blue dye adsorption onto activated carbon, graphene oxide, and carbon nanotubes. Chem. Eng. Res. Des. 2013, 91, 361–368. [Google Scholar] [CrossRef]
  38. Yao, Y.; Xu, F.; Chen, M.; Xu, Z.; Zhu, Z. Adsorption behavior of methylene blue on carbon nanotubes. Bioresour. Technol. 2010, 101, 3040–3046. [Google Scholar] [CrossRef]
  39. Deng, H.; Lu, J.; Li, G.; Zhang, G.; Wang, X. Adsorption of methylene blue on adsorbent materials produced from cotton stalk. Chem. Eng. J. 2011, 172, 326–334. [Google Scholar] [CrossRef]
  40. Fan, L.; Luo, C.; Li, X.; Lu, F.; Qiu, H.; Sun, M. Fabrication of novel magnetic chitosan grafted with graphene oxide to enhance adsorption properties for methyl blue. J. Hazard. Mater. 2012, 215–216, 272–279. [Google Scholar] [CrossRef]
Figure 1. (a) Scanning electron microscope (SEM) of molybdenum oxide (MoO3) nanowires at high resolution (diameter distribution inset); (b) SEM of MoO3 nanowires at low resolution (length distribution inset); (c) Transmission electron microscope (TEM) of MoO3 nanowires; (d) corresponding selected-area electron diffraction (SAED) pattern; (e) X-ray diffraction (XRD) patterns of MoO3 nanowires.
Figure 1. (a) Scanning electron microscope (SEM) of molybdenum oxide (MoO3) nanowires at high resolution (diameter distribution inset); (b) SEM of MoO3 nanowires at low resolution (length distribution inset); (c) Transmission electron microscope (TEM) of MoO3 nanowires; (d) corresponding selected-area electron diffraction (SAED) pattern; (e) X-ray diffraction (XRD) patterns of MoO3 nanowires.
Micromachines 10 00586 g001
Figure 2. The prepared MoO3-based membrane (5 μm) was used to vacuum-filtrate the dyes at different concentrations (ppm): (a) 10 ppm of methylene blue (MB); (b) 10 ppm of rhodamine B (RhB); (c) 10 ppm of methyl orange (MO); (d) adsorption percentage in ppm for different dyes; (e) FT-IR spectrum of the membrane: dyes adsorbed; (f) FT-IR spectrum of the membrane: dyes desorbed.
Figure 2. The prepared MoO3-based membrane (5 μm) was used to vacuum-filtrate the dyes at different concentrations (ppm): (a) 10 ppm of methylene blue (MB); (b) 10 ppm of rhodamine B (RhB); (c) 10 ppm of methyl orange (MO); (d) adsorption percentage in ppm for different dyes; (e) FT-IR spectrum of the membrane: dyes adsorbed; (f) FT-IR spectrum of the membrane: dyes desorbed.
Micromachines 10 00586 g002
Figure 3. The MoO3-based membrane (5 μm) was tested to measure its ability to selectively separate various dyes at 10 ppm: (a) MB + MO; (b) RhB + MO; (c) MB + RhB; (d) Adsorption capacity for various dyes.
Figure 3. The MoO3-based membrane (5 μm) was tested to measure its ability to selectively separate various dyes at 10 ppm: (a) MB + MO; (b) RhB + MO; (c) MB + RhB; (d) Adsorption capacity for various dyes.
Micromachines 10 00586 g003
Figure 4. Reusability of the MoO3 nanowire-based membrane for dye (MB, RhB, MO) adsorption.
Figure 4. Reusability of the MoO3 nanowire-based membrane for dye (MB, RhB, MO) adsorption.
Micromachines 10 00586 g004
Scheme 1. Process of selective adsorption of cationic dyes from blended dyes.
Scheme 1. Process of selective adsorption of cationic dyes from blended dyes.
Micromachines 10 00586 sch001
Table 1. Maximum adsorption abilities of MB for various adsorbents.
Table 1. Maximum adsorption abilities of MB for various adsorbents.
Adsorbent.pHTemp/Kqmax (mg/g)References
Activated carbon7.029391.0[35]
Graphene Oxide6.0298243.9[37]
Carbon nanotubes7.029846.2[38]
Cotton stalk7.0308147.06[39]
Chitosan/graphene oxide5.330395.16[40]
MoO3 nanowires7.0298521.0This study

© 2019 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (
Back to TopTop