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Article

Polydopamine-Assisted Two-Dimensional Molybdenum Disulfide (MoS2)-Modified PES Tight Ultrafiltration Mixed-Matrix Membranes: Enhanced Dye Separation Performance

by
Huali Tian
1,2,
Xing Wu
3 and
Kaisong Zhang
1,*
1
Key Laboratory of Urban Pollutant Conversion, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen 361021, China
2
University of Chinese Academy of Sciences, Beijing 100049, China
3
CSIRO Manufacturing, Clayton South, VIC 3169, Australia
*
Author to whom correspondence should be addressed.
Membranes 2021, 11(2), 96; https://doi.org/10.3390/membranes11020096
Submission received: 22 December 2020 / Revised: 25 January 2021 / Accepted: 26 January 2021 / Published: 30 January 2021
(This article belongs to the Special Issue Nanostructured Membranes II)
Browse Figures
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Abstract

:
Tight ultrafiltration (TUF) membranes with high performance have attracted more and more attention in the separation of organic molecules. To improve membrane performance, some methods such as interface polymerization have been applied. However, these approaches have complex operation procedures. In this study, a polydopamine (PDA) modified MoS2 (MoS2@PDA) blending polyethersulfone (PES) membrane with smaller pore size and excellent selectivity was fabricated by a simple phase inversion method. The molecular weight cut-off (MWCO) of as-prepared MoS2@PDA mixed matrix membranes (MMMs) changes, and the effective separation of dye molecules in MoS2@PDA MMMs with different concentrations were obtained. The addition amount of MoS2@PDA increased from 0 to 4.5 wt %, resulting in a series of membranes with the MWCO values of 7402.29, 7007.89, 5803.58, 5589.50, 6632.77, and 6664.55 Da. The MWCO of the membrane M3 (3.0 wt %) was the lowest, the pore size was defined as 2.62 nm, and the pure water flux was 42.0 L m−2 h−1 bar−1. The rejection of Chromotrope 2B (C2B), Reactive Blue 4 (RB4), and Janus Green B (JGB) in aqueous solution with different concentrations of dyes was better than that of unmodified membrane. The separation effect of M3 and M0 on JGB at different pH values was also investigated. The rejection rate of M3 to JGB was higher than M0 at different pH ranges from 3 to 11. The rejection of M3 was 98.17–99.88%. When pH was 11, the rejection of membranes decreased with the extension of separation time. Specifically, at 180 min, the rejection of M0 and M3 dropped to 77.59% and 88.61%, respectively. In addition, the membrane had a very low retention of salt ions, Nacl 1.58%, Na2SO4 10.52%, MgSO4 4.64%, and MgCl2 1.55%, reflecting the potential for separating salts and dyes of MoS2@PDA/PES MMMs.

1. Introduction

Tight ultrafiltration (TUF) membranes have received increasing attention from water treatment and resource recovery in recent years [1]. Especially in the treatment of dye wastewater, the TUF membrane of mesoporous shows more beneficial effects than nanofiltration (NF) membranes, not only because of the relative lower operating pressure required by the TUF process, but also because of the pore size characteristics of TUF membranes. The sieving effect plays a major role. The dye molecules could be intercepted and the salt ions pass through the membrane pores. Higher purity dye would be obtained. However, due to the combined effect of the sieving effect, dissolution diffusion, and Donan effect [2], traditional nanofiltration (NF) membranes often have a high retention rate of divalent salt ions, which will increase the difficulty of further separation of salt and dye. The TUF membrane is actually a type of ultrafiltration membrane (UF) with a molecular weight cut-off (MWCO) of 1000–10,000 Da and pore size of ≈2–10 nm. To achieve the small pore size, a further interfacial polymerization process [3], surface coating [4], surface deposition [5] and membrane porous filling [6] are applied on as-prepared UF membranes. However, considering the limitations of mass production, phase inversion is still the first choice. Without complex polymer modification and complicated preparation procedures, blending with nanoparticles and polymer to prepare a mixed matrix membrane (MMM) is one of the important means to improve the performance of the membrane. However, poor compatibility between nanoparticles and polymers may provide the non-selective voids and have negative impacts on membrane properties and performance such as reducing the retention rate.
To enhance the compatibility between nanoparticles and polymers, dopamine (DA, 3,4-dihydroxyphenethylamine) has become a popular choice in modification research. Inspired by the mussel’s adhesion behavior, DA has been extracted and applied successfully as glue to the surface modification of various organic and inorganic substances [7]. The application of DA has become a promising membrane modification strategy due to its wideness and versatility [8]. DA self-polymerization forms thin and surface-adherent polydopamine (PDA) films on the membrane surface through deposition. It has been reported that the PDA coating could improve the surface hydrophilicity of PES, polyvinylidenefluoride (PVDF), polysulfone (PSF), polytetrafluroethylene (PTFE), and polyethylene (PE) membranes, and enhance the antifouling ability of these membranes [9,10,11]. In addition to the coating, another method of adding DA to the membrane is blending. The blending method can be performed by introducing DA or PDA to the membrane casting solution directly [12]. This method improves the hydrophilicity, permeability, and antifouling performance of the membrane, increases the porosity and pore size of the membrane. However, the increase in porosity brings great defects to the membrane, such as permeate purity and mechanical properties [13]. In some cases, PDA-encapsulating nanoparticles were blended into the polymer mixed matrix to improve the membrane performance. PDA builds up an intermediate layer around the surface of nanoparticles, enhances the interface compatibility, and reduces the defects of MMMs [14]. Ndlwana et al. blended PDA-crosslinked graphene nanoplatelets (GNP-PDA) to polyethersulfone (PES) MMMs for improved mechanochemical properties [15]. Zhang et al. blended PDA-coated metal–organic frameworks (MOFs) into hydrophilic polymer polyvinyl alcohol (PVA) to enhance the water permeability and selectivity of the MMMs [16]. Sianipar et al. found that the incorporation of PDA-coated multi-walled carbon nanotubes (MWNTs) could increase the membrane permeability without a reduction of selectivity as well as improve the antifouling properties, and enhanced mechanical strength was also found by adding PDA-coated MWNTs into membranes [17]. Wu et al. blended TiO2@PDA into the PSF casting solution to prepare a UF membrane with catalytic properties. PDA as a free radical scavenging agent improved the antifouling ability of the membranes [18]. Most of these membranes focus on anti-pollution performance, and PDA@NPS has seldom studied the MWCO change in membranes. Molybdenum disulfide (MoS2) is a graphene-like material with a relatively large area. It performs well in RO, NF, and UF membrane and improves the permeation without sacrificing retention [19,20,21].
In this work, polydopamine-modified two-dimensional MoS2 was used as a novelty additive to regulate the MWCO of the TUF membrane. The impact of MoS2@PDA on PES-based TUF membranes was investigated by fabricating a series of MoS2@PDA/PES mixed matrix TUF membranes via the simple phase inversion method. In the optimized MoS2@PDA concentration conditions, the MoS2@PDA/PES membrane has better stability, smaller pore size, and better dye selectivity than pristine membrane. The morphology structure, surface characteristics, membrane thermostability, dyes separation, and salts filtration performance of the prepared membranes were investigated.

2. Experimental

2.1. Materials

Commercial polyethersulfone (PES) Ultrason E6020P was supplied by BASF (BASF, Corp., Ludwigshafen, Germany). Molybdenum sulfide (MoS2) (99.5% metals basis, <2 μm) (Aladdin, Inc., Shanghai, China). N,N-Dimethylacetamide (DMAc) and Polyvinylpyrrolidone (PVP K30) (Sinopharm, Inc., Shanghai, China). DA hydrochloride, Polyethylene glycol PEG (2000, 4000, 6000, 8000, 10,000 Da), Chromotrope 2B (C2B) (513.37 Da), Reactive Blue 4 (RB4) (637.43 Da), and Janus Green B (JGB) (511.06 Da) were acquired from Sigma Aldrich (Sigma–Aldrich, Inc., St. Louis, MO, USA) Deionized (DI) water was used in all experiments.

2.2. Synthesis of MoS2@PDA

To prepare MoS2@PDA (Figure 1), 0.5 g of MoS2 sheets were dispersed in 100 mL of 10 mM Tris-buffer (pH ≈ 8.5) by ultrasonic for 4 h to form a suspension solution. Then, 0.3 g DA hydrochloride was added to the suspension solution, stirred rapidly for 30 min, and then changed to low-speed agitation for another 24 h at normal temperature. Subsequently, the mixing solution was centrifuged, and the product was washed three times with DI water and ethanol, and then dried in an oven at 60 °C. This product was labeled as MoS2@PDA.

2.3. Membrane Preparation

Table 1 lists the components of different casting solutions. Different contents of MoS2@PDA powders were added into the DMAc solution and sonicated for 30 min to form the MoS2@PDA uniform dispersion solution. After that, PVP and PES were added into the MoS2@PDA solution, and the mixture was stirred at 60 °C until a homogeneous solution was formed. The casting solution was poured on a non-woven fabric on a glass plate. A casting knife gap setting of 200 μm was applied to control the thickness of membranes, and the casting process was conducted under a temperature of 25 °C and humidity of 45 ± 5%. After casting, the plate was immersed into a DI water bath. Finally, the prepared membrane was transferred to fresh pure water for 24 h to remove the residue and then stored in DI water prior to use.

2.4. Characterization of MoS2@PDA

The morphological structure of MoS2 and MoS2@PDA was characterized by field emission transmission electron microscopy (FETEM, Tecnai F20-, FEI Corp., Portland, OR, USA). The hydrophilicity of nanomaterials was determined by a contact goniometer by dropping 2.0 µL of water (CA, DSA100, Krüss Company, Ltd., Hamburg, Germany). The zeta potential of MoS2 and MoS2@PDA was measured using zeta potential (Zeta PALS, Malvern Instruments Ltd., Malvern, UK). The pH was adjusted in the range of 3 to 11 by NaOH and HCl solution. Thermogravimetric analyses (TGA, Perkin Elmer) were conducted under nitrogen atmosphere with a flow rate of 60 mL min−1. The sample was placed in a ceramic crucible; the heating temperature ranged from 40 to 1000 °C at a heating rate of 10 °C min−1. The crystal structure was tested by X-ray diffraction (XRD, X’Pert Pro, PANalytical, Netherlan) at a scanning rate of 10° min−1 in the 2θ range of 10–70°. The chemical structure of MoS2 and MoS2@PDA was analyzed by Fourier transform infrared spectroscopy (FTIR, Nicolet iS10, Thermo Fisher Scientific Inc., Waltham, MA, USA). X-ray photoelectron spectrometry (XPS, ESCALAB 250XI, Thermo Fisher Scientific Inc., Waltham, MA, USA) was used to characterize the surface elemental composition of MoS2 and MoS2@PDA.

2.5. Membrane Characterization

To verify the existence of MoS2@PDA in the MoS2@PDA/PES membranes, field emission scanning electron microscopy (FESEM, HITACHIS-4800, Hitachi Co. Ltd., Tokyo, Japan) was used to observe the structural changes of membrane surface and cross-section at 5.0 kV. Before FESEM observation, the dry membrane sample was sputtered with gold. The surface roughness of membranes was determined with atomic force microscope (AFM, Dimension 3100, Bruker Corp., Santa Barbara, CA, USA). The test area is 5 µm × 5 µm. Average values of roughness for the membrane samples were obtained by measuring three different locations. The surface electrical properties were tested using an electro kinetic analyzer (SurPASS3, Anton Paar, Graz, Austria). The pH was adjusted in the range of 3 to 11 by adding NaOH and HCl solution, and 1 mM KCl solution was used as the electrolyte solution. TGA and XPS were applied for analyzing the characteristics of the as-prepared membranes.

2.6. Molecular Weight Cut-Off and Filtration Performance of Membranes

The MWCO of membranes were defined using the different molecular weights of polyethylene glycols (PEGs), which were retained with 90% [22]. The test was performed using a dead-end filtration system (Model 8050, Millipore Corp., Burlington, MA, USA) at 0.1 MPa. First, 50 mL of 1.0 gL−1 PEG solution was used as the feed liquid. The filtration process was completed when ≈20% of feed solution (i.e., 10 mL) was filtrated through the membrane. Both the feed and permeate solution were diluted by 10 times, and then, the concentration of each solution was tested by a total organic carbon analyzer (TOC, TOC-LCSH, Shimadzu, Japan) [23]. The PEG rejection was calculated using Equation (1):
R ( % ) = ( 1 − C p C f ) × 100
where Cp and Cf are the PEG concentrations of permeate and feed solutions respectively (gL−1). It was reported that the mean effective pore size of the membrane equals the Stokes radius (ds) of PEG at 50% rejection, which could be calculated by Equations (2) and (3) [24]:
r s = 16.73 × 10 − 12 × M P E G 0.557
d s = 2 × r s .
The pore size distribution of the membrane was analyzed by Equation (4).
d R ( d p ) d d p = 1 d p l n σ p 2 π e x p [ ( l n d p − l n u p ) 2 2 ( l n σ p ) 2 ]
where rs and ds stand for the Stokes radius and diameter of the PEG, respectively. MPEG is the MWCO of PEG. The geometric mean diameter (μs) can be calculated as ds corresponding to R = 50%, and the geometric standard deviation (σg) can be determined from the ratio of ds at R = 84.13% and R = 50%. By ignoring the dependence of solute separation on the spatial and hydrodynamic interaction between the solute and the pore size, the average effective pore size (μp) and geometric standard deviation (σp) of the membrane can be regarded as the same as the value of μs and σg [25,26].
The water flux was measured by a dead-end filtration cell with a volume capacity of 50 mL. The effective area of the membrane was 13.4 cm2. Membrane samples were firstly pre-pressed at 0.15 MPa for 30 min, ensuring that the pure water flux reached a steady state; then, we recorded the permeate weight by an electronic balance with Wedge software at 0.1 MPa. The permeate flux (J) was calculated with Equation (5):
J 0 = Δ V A m Δ t
where J 0 (L m−2 h−1) is the membrane flux, Δ V (L) is the volume of permeated water, A (m2) is the membrane area, and Δ t (h) is the permeation time.
The separation performances of the membranes were investigated to filtered dye molecules and salts. The concentration of C2B, RB4, and JGB were measured by Ultraviolet-visible (UV-vis) spectrophotometer (Spectra Max M2, Molecular Devices Co., San Jose, CA, USA). The concentrations of NaCl, Na2SO4, MgSO4, and MgCl2 were measured by a conductivity meter (sensION+EC5, HACH). The permeation flux (Jd) and rejection (Rd) of dye were calculated by Equations (1) and (5), respectively.

3. Results and Discussion

3.1. Characterization of MoS2 and MoS2@PDA

The morphology of MoS2 and MoS2@PDA was investigated by FETEM (Figure 2). It can be found that the surface of the MoS2 was smooth. After modification, MoS2@PDA showed many convex coatings in Figure 2d,e. Figure 2b,e show the HRTEM images of MoS2 and MoS2@PDA. It can be observed that the edge structure of MoS2@PDA becomes softened compared to the unmodified MoS2. In addition, the inset images revealed that both MoS2@PDA and MoS2 consist of the hexagonal lattices and the lattice spacing of 0.27 nm, which was corresponding to the (100) lattice plane MoS2 [27]. The energy dispersive spectroscopy (EDS) spectrum shown in Figure 2c,f indicated that a new peak N can be detected on MoS2@PDA.
The surface hydrophilicity was characterized by the water contact angle (CA) analysis. Average values were obtained by measuring three different locations. As shown in Figure 3, the CA of pristine MoS2 was 79.6 ± 3.2°. Impressively, the CA of MoS2@PDA was 55.53 ± 1.2°, which indicated the improved water wettability of MoS2 by PDA coating. The major reason for this improvement was that dopamine contains a large number of hydrophilic amines and hydroxyl groups, which polymerize under alkaline conditions to form PDA and deposit around MoS2, enhancing the surface hydrophilicity and thus reducing the CA [28,29].
The zeta potential characteristic of particles was shown in Figure 4a. Due to the deposition of zwitterionic PDA, at low pH, the amino group of the PDA was protonated. When pH = 3, the potential of MoS2@PDA was −27.65 mV, and that of MoS2 was −35.9 mV. However, with the increase of pH, the potential of MoS2@PDA was lower than MoS2. This was due to the negative charge of the PDA phenol group after deprotonation at high pH, which enhanced the negative charge of modified particles [30].
Figure 4b gives the results from TGA and DTG analysis carried out on MoS2 and MoS2@PDA. There are two distinct stages of mass loss in the TGA curve: ≈100 °C and 100–500 °C, which corresponded to the peaks on the DTG curve at 102 °C, 328 °C for MoS2 and 96 °C, 282 °C for MoS2@PDA. In the temperature range of 500–1000 °C, the mass loss of MoS2 changes slowly, and the mass loss of MoS2@PDA was almost a straight line with a slope [31]. The TGA curve of MoS2 showed a weight loss of 2.10% when the temperature increased from 0 to 1000 °C. It was mainly due to the weight loss caused by the water or other impurities absorbed on the MoS2 [32]. The weight loss rate of MoS2@PDA was 6.36%, which was higher than the pristine MoS2, indicating that the PDA was coated on the MoS2 surface. According to the calculation of the TGA curve of unmodified and modified, the PDA deposition on MoS2 sheets was approximately 4.26%.
The crystallographic structures of the pristine MoS2 and MoS2@PDA composite were characterized by XRD patterns, as shown in Figure 4c. Peaks at 2θ = 14.3°, 29°, 39.6°, 44°, 49.8°, and 60.1° were well associated with MoS2 (JCPDS card no. 37–1492), which can be assigned to (002), (004), (103), (104), (105), and (110) planes, respectively [33,34]. After encapsulation with PDA, there were no new crystallization peaks. The XRD pattern of MoS2@ PDA still had characteristic diffraction peaks at (002), (004), (103), (104), (105), and (110), which showed that before and after PDA wrapped, the crystal structure of MoS2 had not changed [35]. However, the existence of PDA affected the crystallinity of the MoS2 crystal [27]. The introduction of carbon would lead to the reduction of the diffraction peak [36]. Due to the deposition of dopamine, the carbon element increased, the purity of MoS2 crystal decreased, and the intensity of the diffraction peak reduced.
The FTIR spectra of MoS2 and MoS2@PDA are shown in Figure 4d. Compared to the spectra of MoS2, there was a new peak in the spectra of MoS2@PDA. The peak at around 1498 cm−1 was the C=C skeleton vibration peak of the benzene ring from PDA [37]. The peak at 1630 cm−1 was formed by the oxidation of the dobutamine hydroxyl group to the ketone group C=O [38]. The peak at around 3440 cm−1 can be attributed to the stretching vibration of N–H and OH [32]. Compared to pristine MoS2, the hydrophilicity of MoS2@ PDA was enhanced due to PDA deposition, resulting in an enhanced O–H vibration of H2O [31].
The chemical composition of MoS2@PDA was further investigated by XPS analysis. As shown in Figure 5a, the XPS full energy spectrum investigation indicated that Mo, S, C, N, and O elements were present in the hybrid. It was found that the MoS2 characteristic peaks, such as Mo 3d and S 2p, were reduced after the modification of dopamine. However, the intensity of O1s and C1s were enhanced, and we confirmed the production of dopamine-induced polymerization, which was coated on the MoS2 surface. The high-resolution Mo 3d spectra (Figure 5b) had three peaks; 229.34 eV and 232.51 eV related to Mo4+3d5/2 and Mo4+3d3/2, while the peak at 235.59 eV may be derived from the surface oxidation of Mo6+ [36,39]. In the spectra of the high-resolution S 2p (Figure 5c), there were peaks at 162 eV and 163.3 eV corresponding to the bivalent S 2p3/2 and S 2p1/2 (S2−) [40]. There were two peaks in N1 (Figure 5d); the one at 399.9 eV was associated with pyrrolic nitrogen in an indole ring, and the one at 395.3 eV related to the pyridinic resulting from the dopamine functionalization [41,42]. In the MoS2@PDA (Figure 5e), the binding energy of C1s at 284.5 eV was assigned to C–C/C–H bonds, while that at 285.7 eV was assigned to C–O/C–N, respectively [43]. In the original MoS2 (Figure 5g), C1s at 284.9 eV and 286.8 eV was related to C-C and C–O, which may derived from precursors left over from the formation of MoS2. In the analysis of the O 1s, by comparing Figure 5f,h, there were two new peaks in the modified MoS2 531.3 eV, corresponding to Mo–O and 533.23 eV related to the chemisorbed oxygen [44,45]. The binding energy 532.44 eV on MoS2 was related to O-bonding with residual water [46].

3.2. Characterization of MoS2@PDA/PES TUF Membrane

The surface and the cross-sectional morphologies of membranes are shown in Figure 6. With the increase of MoS2@PDA concentration, the influence of MoS2@PDA can be noticed. By adding MoS2@PDA, the surface was no longer as smooth as the pristine one. It was because during phase inversion, MoS2@PDA migrated from the PES matrix to a water bath and appeared on the membrane surface.
The basic membrane in this study was filled with sponge structures, which was achieved by a high additive amount of PVP [47,48]. This single-layered morphology is favorable for the investigation of the influence of particles in the membrane structure. When the concentration of MoS2@PDA was 2.0 wt %, the presence of hydrophilic MoS2@PDA in the casting solution accelerated the solvent–nonsolvent exchange and instantaneous liquid–liquid separation in the casting solution, resulting in the formation of the microvoids structures observed in the M1 membrane [49]. However, the number of macropores was reduced at a higher additive concentration, and the internal structure was more compact, as shown in the cross-section of membranes M3 and M5. This was due to the fact that rheology played a leading role in the increase of the viscosity of the casting solution with the addition of MoS2@PDA, which reduced the phase conversion rate and densified the membrane structure [50]. The morphological characteristic of the cross-section was different from that of the MoS2/PES TUF membrane; the MoS2@PDA/PES TUF membrane displays fewer microvoids, and the supporting layer is dominated by a sponge structure. This provides the possibility of forming smaller MWCO membranes.
The surface roughness of membranes was measured by AFM (Figure 7). Results were obtained by measuring three different points and indicated that the M0 membrane displayed a smooth surface with an average roughness (Ra) value of 1.73 ± 0.18 nm. The addition of MoS2@PDA made the membrane roughness rise rapidly. When the additive amount was 3.0 wt %, the roughness of the M3 membrane was 45.63 ± 2.07 nm. With the concentration of MoS2@PDA increased to 4.5 wt %, the membrane roughness became 48.8 ± 1.27 nm. The membrane surface became rougher. This was related to the hydrophilic MoS2@PDA migration to the direction of coagulation bath in the phase inversion process. The increased of membrane surface roughness was consistent with the observation result of SEM.
The surface charge of membranes is a critical factor to affect the filtration performance of membranes. As shown in Figure 8, the pristine M0 membrane showed negative charges ranging from 3 to 11 as the pH values increased. These negative charges were believed to come from the functional groups of PES (O=S=O) and PVP (O=C–N) [51]. After the introduction of MoS2@PDA, the M3 membrane showed more negative charges than that of the pristine membrane at different pH values, which was caused by the electronegativity of MoS2@PDA.
The TGA analysis was conducted to investigate the thermal stability of the pristine membrane (M0) and the PES/MoS2@PDA membrane (M3). As can be seen from the TGA curves in Figure 8, rapid material losses were observed in both the M0 and M3 membrane as the temperature increased from 400 to 600 °C, which was due to the polymer decomposition of PES [52]. When the analysis temperature reached 1000 °C, the weight loss of the M0 membrane was 81.73%, which was larger than the weight loss of the M3 membrane (75.51%). This indicated that the thermal stability of the membrane was improved after the addition of MoS2@PDA. This was due to the interaction between the MoS2@PDA nanomaterial and PES, which increased the rigidity of the polymer chain and the fracture energy of the polymer chain.

3.3. Performance of MoS2@PDA/PES TUF Membrane

MWCO and Filtration Performance

A series of PEG (PEG 2000 Da, 4000 Da, 6000 Da, 8000 Da) solutions were used as the model molecules. All membranes showed low MWCO values (<7500 Da), indicating the tight characteristic of these membranes. Moreover, the MWCO of membranes was impacted by the blending of MoS2@PDA in casting solutions. When the added concentration of MoS2@PDA was 3.0 wt %, the membrane (M3) had the smallest MWCO value as 5589 Da. The major reason for this trend was that with the addition of nanoparticles, the adsorption between the exposed hydroxyl group on the surface of MoS2@PDA and the polymer chain increased the viscosity of the casting solution, resulting in delayed phase separation [53,54]. It was beneficial to create a denser structure in MoS2@PDA/PES MMM. However, when the concentration of MoS2@PDA further increased, the MWCO increased instead, which was related to the agglomeration of nanoparticles on the membrane structure, and the defects deteriorate the PEG rejection. With the increase of MoS2@PDA concentration, the pure water flux of the membrane decreased from M0 53.67 ± 2.73 L m−2 h−1 bar−1 to M5 34.75 ± 1.5 L m−2 h−1 bar−1. The reduced water flux was directly related to the decreased porosity with the increasing of MoS2@PDA in membranes. With the increase of MoS2@PDA loading, the porosity decreased gradually from 78.50 ± 0.42% for the M0 membrane to 74.02 ± 0.65% for the M5 membrane (Figure 9b). Moreover, compared to the M0 membrane, the MoS2@PDA blended TUF membrane has smaller pore sizes and MWCO values (Figure 9c). The average pore size of the membrane reduced from 2.97 nm for the M0 membrane to 2.62 nm for the M3 membrane. As a result of its smallest MWCO value, the M3 membrane was selected for further evaluation of dye separation performance.
Dye removal experiments were conducted by using three kinds of dyes solution (C2B, RB4, and JGB) with different concentrations (10, 50, and 100 mgL−1). Figure 10 shows the retention performance of different dyes. Figure 10a,c,d shows the separation effect of M3 on 50 mgL−1 dye, displaying the UV-visible spectra of the dye solution before and after the filtration. The obvious difference of colors of the feed solution and permeate solution indicated the high dye rejection performance of the M3 membranes. Moreover, compared with the pristine M0 membrane, the M3 membrane showed better dye retention effects to those dyes. The RB4 and JGB selectivity performances of the M3 membrane were stable even when the dye concentration increased from 10 to 100 mgL−1. However, for the C2B solution, as the dye concentration increased, the membrane retention rate fell from 94.17% to 78.43%. This may be due to the increase of impurities with the increase of dye concentration. The addition of these ions enhanced electrostatic shielding, thus reducing the rejection of the dye [55].
The zeta potential characterization of the membrane is shown in Figure 8a. With the increase of pH, the negative charge on the membrane surface was enhanced, and the zeta potential of the M3 membrane was always lower than that of the M0 membrane. The lower zeta potential for the M3 membrane was more conducive to the adsorption of positively charged dye JGB. Due to the concentration polarization on the membrane surface, the dye retention rate would increase with the increase of pH (Figure 11a) [56]. The membrane’s interception rate of JGB decreased with the extension of filtration time in a longer period of filtration (Figure 11b). As the separation time was extended to 180 min, the JGB rejection of the M3 membrane was 88.61%, while the JGB rejection of the M0 membrane fell to 77.59%, indicating the good stability of the M3 membrane. Figure 11c shows the water flux of the M0 and M3 membranes during the long filtration test. Compared to the M0 membrane, the M3 membrane showed a low water flux reduction rate, which further confirmed the stable dye filtration performance of the M3 membrane. In future work, we will select more types of pollutants with different sizes and involve membrane cleaning cycles to investigate the stability and the service life of the membrane.
The high salinity in the textile wastewater affects the retention of dyes by the membrane. Passing the salt through the membrane is a possible strategy to separate dye and salt in one step. This will save costs for subsequent recovery of dye and salt [57]. The filtration performance of the pristine membrane and MoS2@PDA-modified membrane was further evaluated with different salts (shown in Figure 12). As expected, the rejection of salts was inefficient, showing 0.76%, 10.64%, 4.31%, and 1.99% for NaCl, Na2SO4, MgSO4, and MgCl2, respectively. Accordingly, because M0 and M3 were negatively charged, the low salt rejection could be ascribed to the membrane screening effect. The hydration radius of salt ions was much smaller than the membrane pore size (Na+: 0.36 nm, Mg2+: 0.43 nm, SO42−: 0.38 nm, Cl−: 0.33 nm) [58]. The small-sized ions could be allowed to pass through the membrane pores easily [59].
Figure 13 compared the water flux of the M3 membrane and other TUF membranes with similar MWCO in previous studies. The result indicated that the M3 membrane manufactured in this study had a higher water flux than other TUF membranes with similar MWCO values. All these further revealed that the MoS2@PDA-modified TUF has a high feasibility to be applied for dye separation.

4. Conclusions

This study developed a one-step phase inversion approach to fabricate MoS2@PDA-modified TUF membranes. Improvements of MoS2@PDA on the properties and filtration performance were investigated by varied membrane characterization and performance evaluation. The blending of MoS2@PDA into PES membranes results in a denser membrane structure and enhanced thermal stability and electronegativity. In addition, TUF membranes with different MWCO were obtained by controlling the loading of MoS2@PDA. The membrane with 3.0 wt % MoS2@PDA had a lowest MWCO (5589 Da), showed a good pure water permeation flux as 42.0 Lm−2h−1 bar−1, and had a high rejection of dye JBG up to 99.88% at pH 5. The salt ions removal rate of membrane M3 was mostly lower than 10%, indicating that the membrane provided free salt ions permeation. The MoS2@PDA/PES membrane prepared in this work has the potential to efficiently separate and recover dye and salt.

Author Contributions

Conceptualization, H.T. and K.Z.; methodology, H.T.; software, H.T.; validation, K.Z., H.T. and X.W.; formal analysis, H.T. and X.W.; investigation, H.T.; resources, H.T. and X.W.; data curation, H.T.; writing—original draft preparation, H.T. and X.W.; writing—review and editing, H.T. and X.W.; visualization, H.T. and X.W.; supervision, K.Z.; project administration, K.Z.; funding acquisition, K.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by grants from the Bureau of Frontier Sciences and Education (QYZDB-SSW-DQC044), the Bureau of International Cooperation (132C35KYSB20160018), the Chinese Academy of Sciences and the Joint Project between CAS-CSIRO (132C35KYSB20170051).

Acknowledgments

This work was supported by grants from the Bureau of Frontier Sciences and Education (QYZDB-SSW-DQC044), the Bureau of International Cooperation (132C35KYSB20160018), the Chinese Academy of Sciences and the Joint Project between CAS-CSIRO (132C35KYSB20170051). The authors acknowledge Shishi Yang, Qingliang Jiang, Yili, Temitope Fausat Ajibade, and Fangfang for their assistance in the membrane preparation. The authors also thank the technical help from Zhen Xu for the XPS measurements, Hongyun Ren for the SEM test, Ping Huang for TEM analysis, DanMei Pan for the AFM test.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Lin, J.; Lin, F.; Chen, X.; Ye, W.; Li, X.; Zeng, H.; van der Bruggen, B. Sustainable Management of Textile Wastewater: A Hybrid Tight Ultrafiltration/Bipolar-Membrane Electrodialysis Process for Resource Recovery and Zero Liquid Discharge. Ind. Eng. Chem. Res. 2019, 58, 11003–11012. [Google Scholar] [CrossRef]
  2. Mohammad, A.W.; Teow, Y.H.; Ang, W.L.; Chung, Y.T.; Oatley-Radcliffe, D.L.; Hilal, N. Nanofiltration membranes review: Recent advances and future prospects. Desalination 2015, 356, 226–254. [Google Scholar] [CrossRef]
  3. Tesha, J.M.; Dlamini, D.S.; Qaseem, S.; Cui, Z.; Li, J. Tight ultrafiltration: Layer deposition of Trimesoyl chloride/β-Cyclodextrin onto Polysulfone/Poly (styrene-co-maleic anhydride) membrane for water treatment. J. Environ. Chem. Eng. 2020, 8, 103733. [Google Scholar] [CrossRef]
  4. Fan, W.L.; Li, L.; Guo, F.; Lu, X.F.; Guo, L.W. Primary study of novel poly(acrylic sodium)/poly(ether sulfone) composite ultraltration membranes(I) the preparation of composite membrane. Desalination 2009, 249, 1385–1389. [Google Scholar]
  5. Ye, W.; Ye, K.; Lin, F.; Liu, H.; Jiang, M.; Wang, J.; Liu, R.; Lin, J. Enhanced fractionation of dye/salt mixtures by tight ultrafiltration membranes via fast bio-inspired co-deposition for sustainable textile wastewater management. Chem. Eng. J. 2020, 379, 122321. [Google Scholar] [CrossRef]
  6. Lan, Q.; Wang, Z.; Wang, Y. Mesoporous phenolics filled in macroporous membranes for tunable tight-ultrafiltration. Chem. Eng. Sci. 2018, 187, 98–106. [Google Scholar] [CrossRef]
  7. Lee, H.; Dellatore, S.M.; Miller, W.M.; Messersmith, P.B. Mussel-inspired surface chemistry for multifunctional coatings. Science 2007, 318, 426–430. [Google Scholar] [CrossRef] [Green Version]
  8. Yan, Z.; Zhang, Y.; Yang, H.; Fan, G.; Ding, A.; Liang, H.; Li, G.; Ren, N.; van der Bruggen, B. Mussel-inspired polydopamine modification of polymeric membranes for the application of water and wastewater treatment: A review. Chem. Eng. Res. Des. 2020, 157, 195–214. [Google Scholar] [CrossRef]
  9. Gao, W.J.W.F.; Zhang, H.; Jia, H.; Cui, Z.; Yang, G. Aged PVDF and PSF ultrafiltration membranes restored by functional__polydopamine for adjustable pore sizes and fouling control. J. Membr. Sci. 2019, 570, 156–167. [Google Scholar] [CrossRef]
  10. Zarghami, S.; Mohammadi, T.; Sadrzadeh, M. Preparation, characterization and fouling analysis of in-air hydrophilic/underwater oleophobic bio-inspired polydopamine coated PES membranes for oily wastewater treatment. J. Membr. Sci. 2019, 582, 402–413. [Google Scholar] [CrossRef]
  11. Xi, Z.-Y.; Xu, Y.-Y.; Zhu, L.-P.; Wang, Y.; Zhu, B.-K. A facile method of surface modification for hydrophobic polymer membranes based on the adhesive behavior of poly(DOPA) and poly(dopamine). J. Membr. Sci. 2009, 327, 244–253. [Google Scholar] [CrossRef]
  12. Wang, Z.; Tang, F.; Fan, H.; Wang, L.; Jin, Z. Polydopamine Generates Hydroxyl Free Radicals under Ultraviolet-Light Illumination. Langmuir ACS J. Surf. Colloids 2017, 33, 5938–5946. [Google Scholar] [CrossRef] [PubMed]
  13. Jiang, J.-H.; Zhu, L.-P.; Zhang, H.-T.; Zhu, B.-K.; Xu, Y.-Y. Improved hydrodynamic permeability and antifouling properties of poly(vinylidene fluoride) membranes using polydopamine nanoparticles as additives. J. Membr. Sci. 2014, 457, 73–81. [Google Scholar] [CrossRef]
  14. Liu, Q.; Wang, H.; Wu, C.; Wei, Z.; Wang, H. In-situ generation of iron-dopamine nanoparticles with hybridization and cross-linking dual-functions in poly (vinyl alcohol) membranes for ethanol dehydration via pervaporation. Sep. Purif. Technol. 2017, 188, 282–292. [Google Scholar] [CrossRef]
  15. Ndlwana, L.; Motsa, M.M.; Mamb, B.B. A unique method for dopamine-cross-linked graphene nanoplatelets within polyethersulfone membranes (GNP-pDA/PES) for enhanced mechanochemical resistance during NF and RO desalination. Eur. Polym. J. 2020, 136, 109889. [Google Scholar] [CrossRef]
  16. Zhang, W.; Ying, Y.; Ma, J.; Guo, X.; Huang, H.; Liu, D.; Zhong, C. Mixed matrix membranes incorporated with polydopamine-coated metal-organic framework for dehydration of ethylene glycol by pervaporation. J. Membr. Sci. 2017, 527, 8–17. [Google Scholar] [CrossRef]
  17. Sianipar, M.; Kim, S.H.; Min, C.; Tijing, L.D.; Shon, H.K. Potential and performance of a polydopamine-coated multiwalled carbon nanotube/polysulfone nanocomposite membrane for ultrafiltration application. J. Ind. Eng. Chem. 2016, 34, 364–373. [Google Scholar] [CrossRef]
  18. Wu, H.; Liu, Y.; Mao, L.; Jiang, C.; Ang, J.; Lu, X. Doping polysulfone ultrafiltration membrane with TiO2-PDA nanohybrid for simultaneous self-cleaning and self-protection. J. Membr. Sci. 2017, 532, 20–29. [Google Scholar] [CrossRef]
  19. Li, Y.; Yang, S.; Zhang, K.; van der Bruggen, B. Thin film nanocomposite reverse osmosis membrane modified by two dimensional laminar MoS2 with improved desalination performance and fouling-resistant characteristics. Desalination 2019, 454, 48–58. [Google Scholar] [CrossRef]
  20. Yang, S.; Zhang, K. Few-layers MoS2 nanosheets modified thin film composite nanofiltration membranes with improved separation performance. J. Membr. Sci. 2020, 595, 117526. [Google Scholar] [CrossRef]
  21. Tian, H.; Wu, X.; Zhang, K. Mixed matrix polyethersulfone tight ultrafiltration (TUF) membrane with improved dye removal by physical blending of 2D MoS2. Desalination Water Treat. 2020, 204, 93–106. [Google Scholar] [CrossRef]
  22. Dolar, D.; Kosutic, K.; Strmecky, T. Hybrid processes for treatment of landfill leachate: Coagulation/UF/NF-RO and adsorption/UF/NF-RO. Sep. Purif. Technol. 2016, 168, 39–46. [Google Scholar] [CrossRef]
  23. Wang, K.; Lin, X.; Jiang, G.; Liu, J.Z.; Jiang, L.; Doherty, C.M.; Hill, A.J.; Xu, T.; Wang, H. Slow hydrophobic hydration induced polymer ultrafiltration membranes with high water flux. J. Membr. Sci. 2014, 471, 27–34. [Google Scholar] [CrossRef]
  24. Liu, C.; Mao, H.; Zheng, J.; Zhang, S. In situ surface crosslinked tight ultrafiltration membrane prepared by one-step chemical reaction-involved phase inversion process between activated PAEK-COOH and PEI. J. Membr. Sci. 2017, 538, 58–67. [Google Scholar] [CrossRef]
  25. Singh, S.; Khulbe, K.C.; Matsuura, T.; Ramamurthy, P. Ramamurthy, Membrane characterization by solute transport and atomic force microscopy. J. Membr. Sci. 1998, 142, 111–127. [Google Scholar] [CrossRef]
  26. Li, Y.; Wong, E.; Mai, Z.; van der Bruggen, B. Fabrication of composite polyamide/Kevlar aramid nanofiber nanofiltration membranes with high permselectivity in water desalination. J. Membr. Sci. 2019, 592, 117396. [Google Scholar] [CrossRef]
  27. Wei, Y.; Hu, C.; Muhammad, Y.; Chen, L.; Zhou, D.; Wang, S.; Li, J.; Chen, Q. Fabrication and performance evaluation of aminopropyl triethoxysilane-dopamine-MoS2 incorporated SBS modified asphalt. Constr. Build. Mater. 2020, 265, 120346. [Google Scholar] [CrossRef]
  28. Gao, J.; Zhang, M.; Wang, J.; Liu, G.; Liu, H.; Jiang, Y. Bioinspired Modification of Layer-Stacked Molybdenum Disulfide (MoS2) Membranes for Enhanced Nanofiltration Performance. ACS Omega 2019, 4, 4012–4022. [Google Scholar] [CrossRef] [Green Version]
  29. Wang, Q.; Jia, F.; Song, S.; Li, Y. Hydrophilic MoS2/polydopamine (PDA) nanocomposites as the electrode for enhanced capacitive deionization. Sep. Purif. Technol. 2020, 236, 116298. [Google Scholar] [CrossRef]
  30. Liu, Q.; Yu, B.; Ye, W.; Zhou, F. Highly selective uptake and release of charged molecules by pH-responsive polydopamine microcapsules. Macromol. Biosci. 2011, 11, 1227–1234. [Google Scholar] [CrossRef]
  31. Wang, Y.; Zeng, S.; Sun, K.; Yang, B.; Jia, F.; Song, S. Highly stable MoS2@PDA composite for enhanced reduction of AuCl4−. Chem. Phys. Lett. 2020, 747, 137350. [Google Scholar] [CrossRef]
  32. Zeng, G.; Huang, L.; Huang, Q.; Liu, M.; Xu, D.; Huang, H.; Yang, Z.; Deng, F.; Zhang, X.; Wei, Y. Rapid synthesis of MoS2-PDA-Ag nanocomposites as heterogeneous catalysts and antimicrobial agents via microwave irradiation. Appl. Surf. Sci. 2018, 459, 588–595. [Google Scholar] [CrossRef]
  33. Zheng, J.; Zhang, H.; Dong, S.; Liu, Y.; Nai, C.T.; Shin, H.S.; Jeong, H.Y.; Liu, B.; Loh, K.P. High yield exfoliation of two-dimensional chalcogenides using sodium naphthalenide. Nat. Commun. 2014, 5, 2995. [Google Scholar] [CrossRef] [PubMed]
  34. Saraswathi, M.; Rana, D.; Nagendran, A.; Alwarappan, S. ustom-made PEI/exfoliated-MoS2 nanocomposite ultrafiltration membranes for separation of bovine serum albumin and humic acid. Mater. Sci. Eng. C Mater. Biol. Appl. 2018, 83, 108–114. [Google Scholar] [CrossRef] [PubMed]
  35. Hussain, M.A.; Yang, M.; Lee, T.J.; Kim, J.W.; Choi, B.G. High density decoration of noble metal nanoparticles on polydopamine-functionalized molybdenum disulphide. J. Colloid Interface Sci. 2015, 451, 216–220. [Google Scholar] [CrossRef]
  36. Zhao, H.; Li, J.; Wu, H.; Dong, T.; Zhang, Y.; Liu, H. Dopamine Self-Polymerization Enables an N-Doped Carbon Coating of Exfoliated MoS2 Nanoflakes for Anodes of Lithium-Ion Batteries. ChemElectroChem 2018, 5, 383–390. [Google Scholar] [CrossRef]
  37. Zheng, Y.; Zhang, L.; Shi, J.; Liang, Y.; Wang, X.; Jiang, Z. Mussel-inspired surface capping and pore filling to confer mesoporous silica with high loading and enhanced stability of enzyme. Microporous Mesoporous Mater. 2012, 152, 122–127. [Google Scholar] [CrossRef]
  38. Zhang, C.-M.; Qin, S.-Y.; Cheng, Y.-J.; Zhang, A.-Q. Construction of poly(dopamine) doped oligopeptide hydrogel. Rsc Adv. 2017, 7, 50425–50429. [Google Scholar] [CrossRef] [Green Version]
  39. Abedin, S.Z.E. Role of chromate, molybdate and tungstate anions on the inhibition of aluminiumin chloride solutions. J. Appl. Electrochem. 2001, 31, 711–718. [Google Scholar] [CrossRef]
  40. Yang, J.; Xiao, Q.; Lin, Z.; Li, Y.; Jia, X.; Song, H. Growth of ultra-dense MoS2 nanosheets on carbon fibers to improve the mechanical and tribological properties of polyimide composites. Friction 2020. [Google Scholar] [CrossRef]
  41. Niu, Z.; Zhao, Y.; Sun, W.; Shi, S.; Gong, Y. Biomimetic surface modification of polypropylene by surface chain transfer reaction based on mussel-inspired adhesion technology and thiol chemistry. Appl. Surf. Sci. 2016, 386, 41–50. [Google Scholar] [CrossRef]
  42. Qian, X.; Zhu, G.; Wang, K.; Zhang, F.; Liang, K.; Luo, W.; Yang, J. Bowl-like mesoporous polymer-induced interface growth of molybdenum disulfide for stable lithium storage. Chem. Eng. J. 2020, 381, 122651. [Google Scholar] [CrossRef]
  43. Bai, Z.; Wang, L.; Liu, C.; Yang, C.; Lin, G.; Liu, S.; Jia, K.; Liu, X. Interfacial coordination mediated surface segregation of halloysite nanotubes to construct a high-flux antifouling membrane for oil-water emulsion separation. J. Membr. Sci. 2020, 620, 118828. [Google Scholar] [CrossRef]
  44. Mei, F.; Zhang, J.; Dai, K.; Zhu, G.; Liang, C. A Z-scheme Bi2MoO6/CdSe-diethylenetriamine heterojunction for enhancing photocatalytic hydrogen production activity under visible light. Dalton Trans. 2019, 48, 1067–1074. [Google Scholar] [CrossRef] [PubMed]
  45. Fageria, P.; Sudharshan, K.Y.; Nazir, R.; Basu, M.; Pande, S. Decoration of MoS2 on g-C3N4 surface for efficient hydrogen evolution reaction. Electrochim. Acta 2017, 258, 1273–1283. [Google Scholar] [CrossRef]
  46. Patil, S.J.; Park, J.S.; Kim, Y.-B.; Lee, D.-W. A Quasi 2D Flexible Micro-Supercapacitor Based on MnO2//NiCo2O4 as a Miniaturized Energy-Storage Device. Energy Technol. 2018, 6, 1380–1391. [Google Scholar] [CrossRef]
  47. Ismail, A.F.; Hassan, A.R. Effect of additive contents on the performances and structural properties of asymmetric polyethersulfone (PES) nanofiltration membranes. Sep. Purif. Technol. 2007, 55, 98–109. [Google Scholar] [CrossRef]
  48. Yang, Q.; Chung, T.-S.; Weber, M. Microscopic behavior of polyvinylpyrrolidone hydrophilizing agents on phase inversion polyethersulfone hollow fiber membranes for hemofiltration. J. Membr. Sci. 2009, 326, 322–331. [Google Scholar] [CrossRef]
  49. Huang, H.; Yu, J.; Guo, H.; Shen, Y.; Yang, F.; Wang, H.; Liu, R.; Liu, Y. Improved antifouling performance of ultrafiltration membrane via preparing novel zwitterionic polyimide. Appl. Surf. Sci. 2018, 427, 38–47. [Google Scholar] [CrossRef]
  50. Arefi-Oskoui, S.; Khataee, A.; Safarpour, M.; Vatanpour, V. Modification of polyethersulfone ultrafiltration membrane using ultrasonic-assisted functionalized MoS2 for treatment of oil refinery wastewater. Sep. Purif. Technol. 2020, 238, 116495. [Google Scholar] [CrossRef]
  51. Al Malek, S.A.; Seman, M.N.A.; Johnson, D.; Hilal, N. Formation and characterization of polyethersulfone membranes using different concentrations of polyvinylpyrrolidone. Desalination 2012, 288, 31–39. [Google Scholar] [CrossRef]
  52. Mohshim, D.F.; Mukhtar, H.; Man, Z. A study on carbon dioxide removal by blending the ionic liquid in membrane synthesis. Sep. Purif. Technol. 2018, 196, 20–26. [Google Scholar] [CrossRef]
  53. Yang, Y.; Zhang, H.; Wang, P.; Zheng, Q.; Li, J. The influence of nano-sized TiO2 fillers on the morphologies and properties of PSF UF membrane. J. Membr. Sci. 2007, 288, 231–238. [Google Scholar] [CrossRef]
  54. Evangeline, C.; Pragasam, V.; Rambabu, K.; Velu, S.; Monash, P.; Arthanareeswaran, G.; Banat, F. Iron oxide modified polyethersulfone/cellulose acetate blend membrane for enhanced defluoridation application. Desalination Water Treat. 2019, 156, 177–188. [Google Scholar] [CrossRef] [Green Version]
  55. Jiang, M.; Ye, K.; Deng, J.; Lin, J.; Ye, W.; Zhao, S.; van der Bruggen, B. Conventional Ultrafiltration As Effective Strategy for Dye/Salt Fractionation in Textile Wastewater Treatment. Environ. Sci. Technol. 2018, 52, 10698–10708. [Google Scholar] [CrossRef]
  56. Yu, S.; Liu, M.; Ma, M.; Qi, M.; Lü, Z.; Gao, C. Impacts of membrane properties on reactive dye removal from dye/salt mixtures by asymmetric cellulose acetate and composite polyamide nanofiltration membranes. J. Membr. Sci. 2010, 350, 83–91. [Google Scholar] [CrossRef]
  57. Lin, J.; Ye, W.; Baltaru, M.-C.; Tang, Y.P.; Bernstein, N.J.; Gao, P.; Balta, S.; Vlad, M.; Volodin, A.; Sotto, A.; et al. Tight ultrafiltration membranes for enhanced separation of dyes and Na2SO4 during textile wastewater treatment. J. Membr. Sci. 2016, 514, 217–228. [Google Scholar] [CrossRef]
  58. Wang, T.; He, X.; Li, Y.; Li, J. Novel poly(piperazine-amide) (PA) nanofiltration membrane based poly(m-phenylene isophthalamide) (PMIA) hollow fiber substrate for treatment of dye solutions. Chem. Eng. J. 2018, 351, 1013–1026. [Google Scholar] [CrossRef]
  59. Soyekwo, F.; Liu, C.; Wen, H.; Hu, Y. Construction of an electroneutral zinc incorporated polymer network nanocomposite membrane with enhanced selectivity for salt/dye separation. Chem. Eng. J. 2020, 380, 122560. [Google Scholar] [CrossRef]
  60. Liu, C.; Mao, H.; Zheng, J.; Zhang, S. Tight ultrafiltration membrane: Preparation and characterization of thermally resistant carboxylated cardo poly (arylene ether ketone)s (PAEK-COOH) tight ultrafiltration membrane for dye removal. J. Membr. Sci. 2017, 530, 1–10. [Google Scholar] [CrossRef] [Green Version]
  61. Liu, H.; Chen, Y.; Zhang, K.; Wang, C.; Hu, X.; Cheng, B.; Zhang, Y. Poly(vinylidene fluoride) hollow fiber membrane for high-efficiency separation of dyes-salts. J. Membr. Sci. 2019, 578, 43–52. [Google Scholar] [CrossRef]
  62. Amura, I.F.; Shahid, S.; Sarihan, A.; Shen, J.; Patterson, D.A.; Emanuelsson, E.A.C. Fabrication of self-doped sulfonated polyaniline membranes with enhanced antifouling ability and improved solvent resistance. J. Membr. Sci. 2019, 620, 117712. [Google Scholar] [CrossRef]
  63. Guo, S.; Luo, J.; Yang, Q.; Qiang, X.; Feng, S.; Wan, Y. Decoloration of Molasses by Ultrafiltration and Nanofiltration: Unraveling the Mechanisms of High Sucrose Retention. Food Bioprocess Technol. 2019, 12, 39–53. [Google Scholar] [CrossRef]
  64. Arénillas, M.D.S.; Monnin, E.; Moulin, P. Glycerin removal from ultrafiltration flat sheet membranes by filtration and soaking. J. Memb. Sci. Res. 2017, 3, 102–108. [Google Scholar]
  65. Huang, X.; Tian, C.; Qin, H.; Guo, W.; Gao, P.; Xiao, H. Preparation and characterization of Al3+-doped TiO2 tight ultrafiltration membrane for efficient dye removal. Ceram. Int. 2020, 46, 4679–4689. [Google Scholar] [CrossRef]
  66. Qin, H.; Guo, W.; Xiao, H. Preparation of γ-Al2O3 membranes for ultrafiltration by reverse micelles-mediated sol-gel process. Ceram. Int. 2019, 45, 22783–22792. [Google Scholar] [CrossRef]
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Figure 1. Synthetic scheme of MoS2@PDA (polydopamine) nanoparticles.
Figure 1. Synthetic scheme of MoS2@PDA (polydopamine) nanoparticles.
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Figure 2. TEM images of MoS2 (a,b) and MoS2@PDA (d,e), EDS spectrum of MoS2 (c), and MoS2@PDA (f).
Figure 2. TEM images of MoS2 (a,b) and MoS2@PDA (d,e), EDS spectrum of MoS2 (c), and MoS2@PDA (f).
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Figure 3. Water contact angles of MoS2 (a) and MoS2@PDA (b).
Figure 3. Water contact angles of MoS2 (a) and MoS2@PDA (b).
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Figure 4. Zeta potential (a), Thermogravimetric analyses (TGA)-DTG curves (b), X-ray diffraction (XRD) characteristic (c), and Fourier transform infrared spectroscopy (FTIR) spectra of MoS2 and MoS2@PDA (d).
Figure 4. Zeta potential (a), Thermogravimetric analyses (TGA)-DTG curves (b), X-ray diffraction (XRD) characteristic (c), and Fourier transform infrared spectroscopy (FTIR) spectra of MoS2 and MoS2@PDA (d).
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Figure 5. XPS spectra for MoS2@PDA and MoS2 (a), high-resolution XPS spectra of Mo 3d (b), S 2p (c), N 1s (d), C1s (e), and O 1s (f) for MoS2@PDA and C1s (g) O 1s (h) for MoS2.
Figure 5. XPS spectra for MoS2@PDA and MoS2 (a), high-resolution XPS spectra of Mo 3d (b), S 2p (c), N 1s (d), C1s (e), and O 1s (f) for MoS2@PDA and C1s (g) O 1s (h) for MoS2.
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Figure 6. SEM images of PES and MoS2@PDA/PES membranes (M0, M1, M3, and M5) and MoS2/PES (3.0 wt % of MoS2) mixed matrix membrane (S).
Figure 6. SEM images of PES and MoS2@PDA/PES membranes (M0, M1, M3, and M5) and MoS2/PES (3.0 wt % of MoS2) mixed matrix membrane (S).
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Figure 7. Atomic force microscope (AFM) images of the M0, M3, and M5 membranes.
Figure 7. Atomic force microscope (AFM) images of the M0, M3, and M5 membranes.
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Figure 8. Zeta potential (a) and TGA curves (b) of pristine membrane and PES/MoS2@PDA Membrane.
Figure 8. Zeta potential (a) and TGA curves (b) of pristine membrane and PES/MoS2@PDA Membrane.
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Figure 9. The pure water fluxes and molecular weight cut-off (MWCO) of membranes (a); the porosity of M0, M1, M3, and M5 (b); the pore size distribution of M0 and M3 (c).
Figure 9. The pure water fluxes and molecular weight cut-off (MWCO) of membranes (a); the porosity of M0, M1, M3, and M5 (b); the pore size distribution of M0 and M3 (c).
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Figure 10. UV-vis absorbtion spectra of the feeds and the permeation of dyes for membrane M3: Chromotrope 2B (C2B) (a), Reactive Blue 4 (RB4) (c), and Janus Green B (JGB) (e). The insets are the corresponding photographs of the dye solutions before and after filtration. Rejection of M0 and M3 membrane for different concentrations of dyes C2B (b), RB4 (d), and JGB (f).
Figure 10. UV-vis absorbtion spectra of the feeds and the permeation of dyes for membrane M3: Chromotrope 2B (C2B) (a), Reactive Blue 4 (RB4) (c), and Janus Green B (JGB) (e). The insets are the corresponding photographs of the dye solutions before and after filtration. Rejection of M0 and M3 membrane for different concentrations of dyes C2B (b), RB4 (d), and JGB (f).
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Figure 11. Separation performance of JGB dyes by membrane M0 and M3. Effect of different pH values on the membrane separation performance. (Dye: JGB, pH range: 3–11, and the pH was adjusted with HCl and NaOH) (a); effect of filtration time on rejection in pH 11 solution (b); effect of filtration time on permeation in pH 11 solution (c); M0 and M3 physical images before and after filtering (d).
Figure 11. Separation performance of JGB dyes by membrane M0 and M3. Effect of different pH values on the membrane separation performance. (Dye: JGB, pH range: 3–11, and the pH was adjusted with HCl and NaOH) (a); effect of filtration time on rejection in pH 11 solution (b); effect of filtration time on permeation in pH 11 solution (c); M0 and M3 physical images before and after filtering (d).
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Figure 12. Salts separation performance: rejection measured for different salt solutions (1000 mg/L) (a); permeation flux of salt solution (b); (pressure of 1 bar was applied).
Figure 12. Salts separation performance: rejection measured for different salt solutions (1000 mg/L) (a); permeation flux of salt solution (b); (pressure of 1 bar was applied).
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Figure 13. The TUF membranes with similar MWCO are listed. Water flux of non-commercial polymer TUF membranes in the literature [60,61,62], commercial TUF membranes reported in the literature [63,64], ceramic TUF membranes reported in the literature [65,66] and a MoS2@PDA/PES mixed matrix TUF membrane in this work are compared.
Figure 13. The TUF membranes with similar MWCO are listed. Water flux of non-commercial polymer TUF membranes in the literature [60,61,62], commercial TUF membranes reported in the literature [63,64], ceramic TUF membranes reported in the literature [65,66] and a MoS2@PDA/PES mixed matrix TUF membrane in this work are compared.
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Table
Table 1. The composition of casting solutions for MoS2@PDA/polyethersulfone (PES) tight ultrafiltration (TUF) mixed matrix membranes.
Table 1. The composition of casting solutions for MoS2@PDA/polyethersulfone (PES) tight ultrafiltration (TUF) mixed matrix membranes.
MembranePES (wt %)PVP (wt %)DMAc (wt %)MoS2@PDA (wt %)
M023.016.061.00.0
M123.016.059.02.0
M223.016.058.52.5
M323.016.058.03.0
M423.016.057.04.0
M523.016.056.54.5
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Tian, H.; Wu, X.; Zhang, K. Polydopamine-Assisted Two-Dimensional Molybdenum Disulfide (MoS2)-Modified PES Tight Ultrafiltration Mixed-Matrix Membranes: Enhanced Dye Separation Performance. Membranes 2021, 11, 96. https://doi.org/10.3390/membranes11020096

AMA Style

Tian H, Wu X, Zhang K. Polydopamine-Assisted Two-Dimensional Molybdenum Disulfide (MoS2)-Modified PES Tight Ultrafiltration Mixed-Matrix Membranes: Enhanced Dye Separation Performance. Membranes. 2021; 11(2):96. https://doi.org/10.3390/membranes11020096

Chicago/Turabian Style

Tian, Huali, Xing Wu, and Kaisong Zhang. 2021. "Polydopamine-Assisted Two-Dimensional Molybdenum Disulfide (MoS2)-Modified PES Tight Ultrafiltration Mixed-Matrix Membranes: Enhanced Dye Separation Performance" Membranes 11, no. 2: 96. https://doi.org/10.3390/membranes11020096

APA Style

Tian, H., Wu, X., & Zhang, K. (2021). Polydopamine-Assisted Two-Dimensional Molybdenum Disulfide (MoS2)-Modified PES Tight Ultrafiltration Mixed-Matrix Membranes: Enhanced Dye Separation Performance. Membranes, 11(2), 96. https://doi.org/10.3390/membranes11020096

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