Development of Hybrid Ultrafiltration Membranes with Improved Water

Jun 8, 2017 - Besides, UiO-66-PSBMA nanoparticles in the thin layer provided additional flow paths for water permeation through their hydrophilic poro...
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Development of hybrid ultrafiltration membranes with improved water separation properties using modified super-hydrophilic metal-organic framework nanoparticles Huazhen Sun, Beibei Tang, and Peiyi Wu ACS Appl. Mater. Interfaces, Just Accepted Manuscript • Publication Date (Web): 08 Jun 2017 Downloaded from http://pubs.acs.org on June 11, 2017

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Development of hybrid ultrafiltration membranes with improved water separation properties using modified super-hydrophilic metal-organic framework nanoparticles Huazhen Sun, Beibei Tang, and Peiyi Wu* State Key Laboratory of Molecular Engineering of Polymers, Department of Macromolecular Science and Laboratory of Advanced Materials, Fudan University, Shanghai 200433, People’s Republic of China.

KEYWORDS: Metal-organic framework; Postsynthetic modification; Zwitterionic, Hybrid membrane; Ultrafiltration;Water purification

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ABSTRACT: Metal-organic frameworks (MOFs) are intensively being explored as filler materials for polymeric membranes primarily due to their high polymer affinity, large pore volumes, and alterable pore functionalities. But the development of MOFbased ultrafiltration (UF) membranes for water treatment lags behind. Herein, poly(sulfobetaine methacrylate) (PSBMA)-functionalized MOF UiO-66-PSBMA was developed, and incorporated into polysulfone (PSf) casting solution to fabricate novel hybrid UF membranes via phase-inversion method. The resultant UiO-66-PSBMA/PSf membrane exhibited significantly improved water flux (up to 602 L m-2 h-1), which was 2.5 times of the pristine PSf membrane (240 L m-2 h-1) and 2 times of UiO-66-NH2/PSf membrane (294 L m-2 h-1), whereas the rejection of UiO-66-PSBMA/PSf membrane was still maintained at a high level. Moreover, UiO-66-PSBMA/PSf membrane exhibited an improved anti-fouling performance. The improvement of membrane performances could be attributed to the well-tailored properties of UiO-66-PSBMA. On one hand, the excellent dispersion and compatibility of UiO-66-PSBMA made sure the formation of a uniform structure with few defects. On the other hand, the superhydrophilicity of UiO-66-PSBMA could accelerate the exchange rate between solvent and non-solvent, resulting in a more hydrophilic surface and a more porous structure. Besides, UiO-66-PSBMA nanoparticles in the skin layer provided additional flow paths for water permeation through their hydrophilic porous structure as well as the tiny interspace between PSf matrix. This study indicates the great application potential of UiO-66-PSBMA in fabricating hybrid UF membranes, and provides a useful guideline to integrate other modified hydrophilic MOFs to design UF membranes for water 2

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treatment.

1 INTRODUCTION Compared with conventional separation technologies, membrane separation exhibits its unique superiority in water desalination and purification owing to its high separation efficiency, simple operation, low cost, and eco-friendliness.1,2 Ultrafiltration (UF), as a pressure-driven separation process, has attracted significant attention in membrane separation because of its excellent performance in the removal of proteins, bacteria, and organic particles.3,4 An ideal UF membrane should possess high water permeability, suitable selectivity as well as excellent anti-fouling property. In fact, hydrophilic modification of UF membranes has been proven to be a common and effective approach for improving their overall properties, especially water permeability and anti-fouling ability. The high hydrophilicity always helps to reduce the flow resistance and suppress the adhesion of contaminants.5,6 Thus, to achieve a highly hydrophilic UF membrane, various inorganic materials, such as SiO2,7 TiO2,8,9 graphene oxide (GO),10,11 ZnO12 and carbon nanotubes (CNTs) 13,14 have been used to fabricate hybrid UF membranes. It is found that both permeability and antifouling performance could be significantly improved after incorporating these inorganic materials into polymer membranes. Metal-organic frameworks (MOFs), as unique crystalline porous materials, built from metal ions and organic linker molecules, have drawn widespread attention. Compared with those traditional inorganic materials, the main advantage of MOFs lies 3

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in their better compatibility with the soft polymer matrices, high surface area as well as controlled porosity.15,16 These advantages can lead to the MOF/polymer hybrid membranes with improved permeability along with well-maintained solute rejection. Consequently, they are being intensively explored in membrane science as filler materials for polymeric membranes.17 Shahid et al.18 reported a preparation strategy for hybrid membranes via in-situ growth of zeolitic imidazolate framework-8 (ZIF-8) in a polymer dispersion. The obtained membranes showed improved performance in CO2/CH4 separation. Recently, Sorribas et al.19 prepared thin film nanocomposite (TFN) membranes using several MOFs as filler. The TFN membrane incorporated with MIL101 presented a large permeation increase, but it lost part of selectivity. Since this pioneering work, many other groups have tried to further optimize the application of MOFs in TFN membranes.20,21 These exciting developments show the significant advantages of using MOFs as filler over traditional inorganic nanoparticles. Nevertheless, most hybrid membranes based on MOFs were applied for gas separation and nanofiltration membrane. Few of them have been exploited as UF membranes.22,23 This is mainly due to the hydrophobic nature of most MOFs, which adversely affects the overall performance of the obtained membranes. Additionally, although MOFs possess organic ligands, they are essentially crystals and present the characteristics of an inorganic crystal. It is usually difficult to achieve a homogeneous MOF dispersion and correspondingly a uniform film by direct dispersion of neat MOF particles in a polymer solution.24,25 Even if the MOF dispersion is pre-treated by sonication, aggregates may still be inevitable due to the hydrophobic nature26 and/or strong 4

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interparticle interactions27,28. The relatively better compatibility between MOF particles and polymers can reduce the formation of defective interfaces in polymer/MOF membranes, but the aggregation of MOFs would lead to a negative effect on flux or rejection.29 Thus, neat MOFs may be unfavorable to be merged into polymers to fabricate UF membranes for water treatment. From this point of view, surface modification might provide an effective route to tailor the properties of MOFs for further optimizing the performance of UF membranes. Postsynthetic modification of MOFs is a well-established approach, which could furnish MOFs with various functionalities by chemical modification in the form of small molecules or polymer chains.30,31 After hydrophilic polymers being grafted or coated on MOFs, the hydrophilicity of MOFs could be greatly enhanced, and the strong interparticle interactions were distinctly reduced. In other words, polymer chains around MOF nanoparticles could effectively prevent the aggregation, and improve the dispersibility of MOFs.32,33 Zwitterionic polymers bearing both anionic and cationic groups in the same monomer unit have been widely employed in the fabrication of hybrid water treatment membranes. Up to now, a number of zwitterionic materials have been developed, and further applied in the fabrication of high-performance separation membranes.34,35 It reveals the compatibility between modified inorganic fillers and polymer matrix could be enhanced via the hydrophobic interactions between the hydrophobic chains in the zwitterionic polymers and polymer matrixes.36 What’s more, the abundant hydrophilic groups of the zwitterionic polymer can form a hydration layer via electrostatic interactions and hydrogen bonds. Consequently, the permeability and 5

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anti-fouling performance of hybrid membranes could be efficiently promoted.37,38 As an important type of MOFs, the amino-derived MOFs provide great opportunities to covalently attach functional groups by postsynthetic modification and the UiO-66-NH2 family has been extensively studied due to their excellent chemical and hydrothermal stabilities. In this study, PSBMA, a representative zwitterionic polymer, was firstly grafted onto the surface of UiO-66-NH2 (UiO-66-PSBMA) via atom transfer radical polymerization (ATRP) procedure (Fig 1B). Then UiO-66PSBMA was incorporated into PSf to prepare hybrid UF membranes via phase inversion. The grafting of PSBMA on UiO-66-NH2 particles could efficiently suppress the aggregation tendency of raw MOFs, thus a homogeneous dispersion of UiO-66PSBMA in casting solution could be obtained. The compatibility between PSf matrix and UiO-66-PSBMA was also enhanced via the hydrophobic interactions between the hydrophobic chains in PSBMA and PSf matrix. More importantly, the superhydrophilicity of UiO-66-PSBMA originated from the abundant hydrophilic groups of PSBMA benefited the hybrid membrane’s hydrophilicity and the formation of more porous structure as well. Last but not least, the highly-ordered porous structure with the aperture size around 6.0 Å (the size of water molecules is ~2.8 Å) of UiO-66-NH2 and its enhanced hydrophilic particle surface are essential for the high flux.39,40 The uniformly dispersed UiO-66-PSBMA particles in the skin layer provided additional flow paths through its hydrophilic porous structure as well as the tiny interspace between PSf matrix .41 As a result, the permeability and anti-fouling performance of UiO-66-PSBMA/PSf hybrid membranes were significantly promoted, compared to 6

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those of the pristine PSf, PSBMA/PSf, and UiO-66-NH2/PSf membranes. Meanwhile, the rejections of the composite membranes were well-retained.

2 EXPERIMENTAL SECTIONS 2.1 Materials. Commercial polysulfone (Udel P3500) was purchased from Boji Co., Ltd. 2-aminoterephthalic acid (H2BDC-NH2), ZrCl4, α-bromoisobutyryl bromide (BiBB), triethylamine (TEA), 2,2’-bipyridine (bpy), CuBr, N-Methyl-2-pyrrolidone (NMP), formic acid were bought from Aladdin Co., Ltd. Sulfobetaine methacrylate (SBMA) was purchased from Sigma-Aldrich. Absolute methanol, CH2Cl2, dimethylformamide (DMF), and bovine serum albumin (BSA) were provided by Sinopharm Chemical Reagent Co., Ltd. All the chemicals were used without further purification. 2.2 Synthesis of inorganic particles Preparation of UiO-66-NH2. ZrCl4 (0.52g) and H2BDC-NH2 (0.17g) were dissolved in a mixed solution of DMF (8 mL) and formic acid (0.8 mL) by sonication. Then the mixture was kept static standing at 120 oC for 24 h inside a 25 mL autoclave. The obtained precipitate was collected by centrifugation and washed with DMF and methanol for 3 times, respectively. Whereafter, the crystals were further immersed in methanol for 2 days for the solution exchange. After being dried under reduced pressure for 12 h at 80 oC, UiO-66-NH2 was obtained. The preparation sketch was illustrated in Figure 1A. Preparation of Br-functionalized UiO-66-NH2 (UiO-66-BiBB). UiO-66-BiBB was 7

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prepared by the acylation reaction between BiBB and UiO-66-NH2 (Figure 1B).42 In a typical procedure, as-prepared UiO-66-NH2 (600 mg) was dispersed in anhydrous CH2Cl2 (100 mL) via sonication. TEA (1.5 mL) and BiBB (2 mL) were dissolved in CH2Cl2 (20 mL), respectively. First, the TEA solution was injected into the UiO-66NH2 suspension. Then the BiBB solution was added into the suspension drop by drop under stirring in an ice-water bath. The mixture was stirred at 50 oC for 24 h. Subsequently, the product was washed thoroughly with CH2Cl2 over 24 h and then dried under reduced pressure at 60 oC. Preparation of UiO-66-PSBMA. UiO-66-PSBMA was prepared through an atom transfer radical polymerization (ATRP) procedure,43 which was illustrated in Figure 1B. To be specific, UiO-66-BiBB (100 mg) was dispersed in the mixture of water (30 mL) and methanol (30 mL) by sonication. After the addition of bpy (122.7 mg) and (1 g) SBMA monomer into the UiO-66-BiBB suspension, the solution was degassed for three times through the typical freeze-pump-thaw process. Then, CuBr (21.6 mg) was added into the above solution and the whole system was degassed for another three times. The reaction was carried out at 60 oC for 24 h. The obtained suspension was purified by dialysis (cut-off MW=14000) for 1 week and a light yellow solution was obtained. Finally, the product was lyophilized and stored in a dryer before use.

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Figure 1. Illustration of the synthesis processes of (A) UiO-66-NH2 and (B) UiO-66PSBMA 2.3 Membrane preparation. The UF membranes were prepared by a phase-inversion method as described in our previous works.44,45 First, a given quantity of UiO-66PSBMA based on the weight of polymer was dispersed in NMP and sonicated for 20 min. Then, PSf was added into the above solution to form a homogeneous solution by stirring. Next, the mixture was further sonicated for 60 min and stirred for 30 min. After removing air bubbles, this solution was cast onto a glass plate. Then, the glass plate was immersed in deionized water at 30 oC for at least 24 h. Finally, the obtained membrane was washed repeatedly with deionized water and stored in deionized water. For comparison, PSf membrane incorporated with UiO-66-NH2 or PSBMA and the pristine PSf membrane were also prepared via the same procedures. 2.4 Characterization Characterization of nanoparticles. Fourier transform infrared spectroscopy (FT-IR) was measured on Nicolet Nexus 470. X-ray diffraction (XRD) patterns were collected

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by a PANalytical X’Pert diffractometer with Cu Kα radiation. Transmission electron microscopy (TEM) images were obtained via a JEOL JEM2100. Thermogravimetric analysis (TGA) was carried out under air atmosphere with a PerkinElmer thermal analyzer at a heating rate of 20 oC/min. X-Ray photoelectron spectroscopy (XPS, Kratos Axis Ultra DLD, Al Kα) was applied to characterize the chemical components. FE-SEM (field-emission scanning electron microscope, Zeiss, Ultra 55) was operated at a working voltage of 20 kV to observe the morphologies of nanoparticles. Characterization of the membranes. The Surface compositions of the as-prepared membranes were determined by X-ray photoelectron spectroscopy (XPS, PHI 5000C&PHI5300). The cross-sectional and surface morphologies of all the membranes were observed by FE-SEM. All the samples were coated with gold before the observation. Element analysis was measured by energy-dispersive spectrometer (EDS) equipped by the aforementioned FE-SEM. The atomic force microscopy (AFM) images were obtained by tapping mode on a Multimode 8. The hydrophilicity of the membranes was characterized by the contact angle using water as the probe liquid. The static water contact angles of the membranes were measured by using OCA15 (Datapyysics CO., Germany). The result for every sample was calculated by averaging at least three values obtained from different areas of the sample. The porosity of the membranes was determined by the classic gravimetric method. It could be calculated via equation (1): Porosity (%) =

𝑊𝑤𝑒𝑡 − 𝑊𝑑𝑟𝑦 𝐴𝐿𝜌

× 100%

(1) 10

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where Wwet and Wdry are the weights of the wet membrane and dry membrane, respectively; ρ is the pure water density; A is the membrane sample area, L is the membrane sample thickness. The pure water flux and protein rejection of membrane were measured using a cross-flow membrane module as shown in Figure S1. The photograph of the cross-flow cell is shown in Figure S2. The efficient filtration area is 26.2 cm2 and the operation pressure was maintained at 0.2 MPa. Then the pure water flux (F) could be calculated via equation (2): F

V A t

(2)

where V is the volume of the permeated pure water; A is the effective membrane area, and t is the operation time. The rejection to BSA (R) was measured using 0.5 g/L BSA solution. And the results can be calculated by the equation (3): R  1

Cp Cf

(3)

where Cp and Cf were the concentrations of the permeation and feed solutions, respectively. They were determined by an ultraviolet-visible spectrophotometer (Lambda 35, PerkinElmer, USA) at 280 nm. Anti-fouling experiments were conducted as follows. The operation pressure here was 0.2 MPa during the whole process. Firstly, distilled water was passed through the membranes for 60 min, and the water flux (J1) reached a stable stage. Secondly, 0.5 g/L BSA solution (pH=4.7, PBS buffer solution) was filtrated for 60 min, and the flux for BSA solution (Jp) was recorded. Then, the membranes were washed with deionized water for 10 min. The pure water flux of cleaned membranes (J2) was measured again. 11

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The flux recovery ratio (FRR), irreversible fouling ratio (Rir), and reversible fouling ratio (Rr) were calculated via the equations (4~6): J2 J1 J1  J 2 Rir  J1 J 2  Jp Rr  J1 FRR 

(4) (5) (6)

3 RESULTS AND DISCUSSION 3.1 Characterization of UiO-66-NH2, UiO-66-BiBB and UiO-66-PSBMA. Figure 2A reflects the XPS spectra of UiO-66-NH2, UiO-66-BiBB and UiO-66-PSBMA. It is found that raw UiO-66-NH2 includes the peaks of C1s (286 eV), O1s (532 eV), N1s (400 eV) and Zr3d (184 eV), which agrees well with the chemical structure of UiO-66NH2.46 There is no signal of Br of unmodified UiO-66-NH2, while a new peak at 70 eV (corresponded to Br3d) shows up in the XPS spectrum of UiO-66-BiBB. This implies that initiator is successfully anchored onto UiO-66-NH2. Zr, N and S signals are almost undetectable in the XPS spectrum of UiO-66-PSBMA, which could be attributed to the successful grafting of PSBMA polymer brushes onto UiO-66-NH2. With respect to the FTIR spectrum of UiO-66-PSBMA (Figure 2B), the characteristic peaks at 1173 and 1041 cm-1 which are assigned to the symmetric and asymmetric stretching of O=S=O from the grafted polymer can be observed. A new peak originated from the C=O stretching vibration of methyl methacrylate from PSBMA appears at 1728 cm-1 as well. Besides, the peak around 2970 cm-1 attributed to the C-H stretching vibration of the methyl groups from PSBMA emerges in the spectra of UiO-66-PSBMA. In short, both 12

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FTIR and XPS results confirm the successful grafting of PSBMA onto UiO-66-NH2 via ATRP.

Figure 2. (A) XPS spectra, (B) FTIR spectra, (C) XRD patterns and (D) TGA results of UiO-66-NH2, UiO-66-BIBB and UiO-66-PSBMA.

The XRD spectra of UiO-66-NH2, UiO-66-BiBB and UiO-66-PSBMA are depicted in Figure 2C, to further investigate the crystallinity of the modified MOFs. The XRD pattern of raw UiO-66-NH2 is remarkably consistent with that reported for the UiO-66 topology.47 The covalent attachment of initiator onto UiO-66-NH2 does not change its crystal structure since UiO-66-BiBB shows the same XRD pattern as that of UiO-66-NH2. For UiO-66-PSBMA, the sharp peaks from raw UiO-66-NH2 are partially overlapped with a wide peak from 10 to 30o, which can be attributed to the amorphous 13

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PSBMA diffraction. The XRD results here also indicate the successful preparation of UiO-66-PSBMA. Figure 2D shows the TGA results of raw UiO-66-NH2 and the modified ones in the air atmosphere. An obvious weight loss from 250 to 350 oC appears in the TGA curve of UiO-66-SPBMA, derived from the decomposition of grafted polymer, and further confirms the successful grafting of PSBMA onto UiO-66NH2 via ATRP. According to the TGA results, the percentage of polymer in UiO-66PSBMA can be estimated as about 54.2%.

Figure 3. TEM images of (A) UiO-66-NH2, (B) UiO-66-BiBB and (C) UiO-66PSBMA. Figure 3 shows the TEM images of UiO-66-NH2, UiO-66-BiBB and UiO-66PSBMA. As shown in Figure 3A and B, UiO-66-BiBB has a similar morphology as the raw UiO-66-NH2 with a particle size of ~50nm. After the polymer modification, the surface of UiO-66-PSBMA becomes smooth (Figure S3) and an obvious polymer shell can even be observed in its TEM image (Figure 3C). Understandably, the core contour and size of UiO-66-PSBMA are similar to those of unmodified UiO-66-NH2. In addition, the prepared UiO-66-PSBMA aqueous solution shows a clear upper critical solution temperature (UCST)-type phase transition, which further confirms the successful preparation of UiO-66-PSBMA (Figure S4). 3.2 Dispersion of UiO-66-PSBMA in the membrane matrix. The compatibility 14

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between inorganic fillers and polymer matrices is considered as one of the greatest challenges during the development of high-performance organic-inorganic hybrid membranes.5,48 Although MOFs, such as UiO-66-NH2 used here, possess organic ligands, they are essentially crystals and present the characteristics of an inorganic crystal. The preparation of a homogeneous MOF dispersion is usually difficult by direct dispersion of raw MOF particles in a polymer solution. As shown in Figure 4B, the PSf casting solution with 0.3 wt% raw UiO-66-NH2 is turbid even after sonication for a long time. This indicates that raw UiO-66-NH2 exhibits a rather poor dispersion in casting solution and aggregation is easily formed. On the contrary, the casting solution with 0.3 wt% UiO-66-PSBMA (Figure 4D) is almost as transparent as the PSBMA/PSf casting solution (Figure 4C). It shows the good dispersity of UiO-66-PSBMA. Understandably, PSBMA brushes formed around MOF nanoparticles can effectively prevent the aggregation and greatly enhance the dispersity. EDS was further employed for the characterization of the dispersion of fillers. The EDS mapping images of the hybrid membrane with 0.3 wt% UiO-66-PSBMA (Figure 5) illustrate that Zr and N elements originated from UiO-66-PSBMA are dispersed uniformly in the whole PSf matrix without obvious aggregation. This result indicates that the PSBMA which wraps on UiO-66-NH2 can effectively improve the compatibility between UiO-66-NH2 and PSf matrix.

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Figure 4. Digital photographs of (A) PSf, (B) 0.3 wt% UiO-66-NH2/PSf, (C) 0.3 wt% PSBMA/PSf and (D) 0.3 wt% UiO-66-PSBMA/PSf casting solutions.

Figure 5. (A) Cross-sectional morphology of UiO-66-PSBMA/PSf membrane with UiO-66-PSBMA loading of 0.3 wt% and the corresponding EDS mapping scanning spectra of (B) C, (C) O, (D) S, (E) Zr, (F) N. 3.3 Characterization of the UiO-66-PSBMA/PSf hybrid membranes. In order to gain a deep insight into the improvement of hybrid membrane by doping UiO-66PSBMA, hybrid membranes with raw UiO-66-NH2 or PSBMA were also prepared, as well as the pristine PSf membrane. The addition content of all the fillers is 0.3 wt%. Membrane surface composition was characterized by XPS analysis. The properties of these membranes were compared in terms of pure water flux, rejection to BSA, crosssectional structure, porosity, surface morphology, and water contact angle.

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Figure 6. XPS spectra of PSf, UiO-66-NH2/PSf, PSBMA/PSf and UiO-66PSBMA/PSf membranes Table 1. Surface elemental percentage of PSf, UiO-66-NH2/PSf, PSBMA/PSf and UiO66-PSBMA/PSf membranes obtained from XPS spectra. Membrane PSf UiO-66-NH2/PSf PSBMA/PSf UiO-66-PSBMA/PSf

C 81.50 81.34 81.46 81.39

Atomic percent (at. %) O S Zr 17.03 1.47 17.00 1.37 0.12 16.06 2.05 16.44 1.80 0.08

N 0.17 0.43 0.29

XPS spectra of the membrane surfaces and the corresponding element contents are shown in Figure 6 and Table 1, respectively. According to Figure 6, the pristine PSf membrane and all the hybrid membranes have peaks for C1s, O1s and S2p. The peaks for the atoms of additives are too weak to be observed due to the small content of them. While, according to Table 1, all of the hybrid membranes contain certain atoms derived from the corresponding additives compared to the pristine PSf membrane. Besides, the element mapping and EDS of the UiO-66-PSBMA/PSf membrane surface show the presence of C, O, S, Zr and N elements (Figure S6). These results confirm the existence of additives on the membrane surfaces.

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Figure 7. (A) Pure water flux and rejections (to BSA) tested at 0.2 MPa operation pressure, (B) contact angle values and (C-F) cross-sectional SEM images of the membranes doping with different fillers. The membrane performances of pure water flux and rejection of hybrid membranes with different fillers are summarized in Figure 7A. All hybrid membranes incorporated with fillers show improved fluxes, compared to that of PSf membrane. And UiO-66-PSBMA/PSf hybrid membrane exhibits the greatest enhancement. In particular, the water flux of UiO-66-PSBMA/PSf is 602 L m-2 h-1, nearly 2.5 times of the pristine PSf membrane (240 L m-2 h-1) and 2 times of UiO-66-NH2/PSf hybrid membrane (294 L m-2 h-1). Meanwhile, the water flux of UiO-66-PSBMA/PSf hybrid membrane is also much higher than that of PSBMA/PSf membrane. These results indicate the existance of synergetic effects between UiO-66-NH2 and PSBMA, and both of them play a nonnegligible role in improving the hybrid membrane’s flux. The cross-sectional and correspondingly magnified cross-sectional images of

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these membranes are displayed in Figure 7 (C-F) and Figure S7, respectively. All the membranes show a typical asymmetric structure, including a dense skin layer and a porous sublayer. The skin layer is responsible for the permeation and rejection whereas the sublayer mainly acts as mechanical support. It is found that the incorporation of UiO-66-PSBMA or PSBMA has influence on both the skin layer and the sublayer. It is found that the finger-like pores of UiO-66-PSBMA/PSf and PSBMA/PSf membranes are longer and wider with total suppression of macrovoids, compared to PSf and UiO66-NH2/PSf membranes. What’s more, the thickness of the skin layer of PSf, UiO-66NH2/PSf, PSBMA/PSf and UiO-66-PSBMA/PSf marked in Figure S7 is ca. 241, 228, 169 and 164 nm, respectively (Table 2). These results are well consistent with the porosity of the membranes (Table 2). It is well-known that the incorporation of hydrophilic nanoparticles into casting solution can accelerate the exchange rate between solvent (NMP) and non-solvent (deionized water) during the coagulation process, thus resulting in a more porous structure.49 The super hydrophilicity of UiO66-PSBMA can be observed by the contact angle dropmeter (Figure S5). Therefore, the incorporation of UiO-66-PSBMA constructs more porous structures compared to the incorporation of raw UiO-66-NH2 due to the super hydrophilicity and excellent dispersibility of UiO-66-PSBMA. The results of the rejection to BSA of the membranes are consistent with these observed structures. In Figure 7A, the rejections of all the hybrid membranes exhibit different degrees of reduction in comparison with pristine PSf membrane. The decrease in rejection of UiO-66-PSBMA/PSf membrane can be attributed to the more porous structure. It is should be noted that the rejection of UiO19

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66-PSBMA/PSf membrane is better retained, compared to that of UiO-66-NH2/PSf membrane. As we all know, the compatibility of fillers in polymer matrices plays an important role in the selectivity of separation membranes. Due to the strong aggregation tendency of raw UiO-66-NH2 that comes from the hydrophobic nature and/or strong interparticle interactions of MOF nanoparticles, the compatibility between UiO-66NH2 and PSf is not good enough, thus resulting in the formation of non-selective voids. Ultimately, the rejection of UiO-66-NH2/PSf membrane declines. After being grafted with hydrophilic PSBMA, the surface of MOF transfers to super hydrophilicity and the interactions are reduced, and a better dispersion of MOF in casting solution can be obtained. As a result, the water flux of UiO-66-PSBMA/PSf hybrid membrane is much higher than that of UiO-66-NH2/PSf membrane.

Figure 8. Surface SEM images of (A) PSf, (B) UiO-66-NH2/PSf, (C) PSBMA/PSf and (D) UiO-66-PSBMA/PSf membranes; AFM three-dimensional surface image of (E) PSf, (F) UiO-66-NH2/PSf, (G) PSBMA/PSf and (H) UiO-66-PSBMA/PSf membranes.

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Table 2. Porosity, skin layer thickness, and the surface roughness values of PSf, UiO66-NH2/PSf, PSBMA/PSf and UiO-66-PSBMA/PSf membranes Membrane PSf UiO-66-NH2/PSf PSBMA/PSf UiO-66-PSBMA/PSf

Porosity (%) 63.2 65.3 68.5 73.4

Skin layer thickness (nm) 241 229 169 164

Rq (nm) 11.8 13.1 16.2 19.3

Ra (nm) 9.7 10.8 13.6 15.3

Moreover, membrane surface morphology and hydrophilicity also play an important role in determining the flux of membranes. A rough surface commonly results in an increase in efficient filtration area, and thereby improving the membrane permeation.50 The roughness of the membrane surface is measured by AFM, which is showed in Figure 8(E-H) and quantified in Table 2. According to the results, UiO-66PSBMA/PSf membrane shows the roughest surface due to the fast exchange rate between NMP and water during the coagulation process, which is consistent with the morphologies by FE-SEM images (Figure 8(E-H)). Contact angles of membranes are used to verify the hydrophilicity change of membranes, and the results are shown in Figure 7B. UiO-66-PSBMA possesses extremely high hydrophilicity due to the grafting of PSBMA.51 As a result, UiO-66-PSBMA/PSf hybrid membrane presents a relatively high hydrophilicity, which is beneficial for the enhancement of water permeability. The contact angles of UiO-66-PSBMA/PSf and PSBMA/PSf exhibit relatively low values (66.3 and 65.7o, respectively). While the contact angle of UiO-66-NH2/PSf (74.8o) is quite close to that of PSf membrane (77.1o). It demonstrates the great promotion effect of UiO-66-PSBMA on membrane hydrophilicity due to the presence of PSBMA, compared to that of raw UiO-66-NH2. The enhanced hydrophilicity undoubtedly is 21

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beneficial to promote water permeation and antifouling properties (discussed later). Note that although the cross-sectional structure and surface properties of PSBMA/PSf membrane are much like those of UiO-66-PSBMA/PSf membrane, its water flux is much lower than UiO-66-PSBMA/PSf membrane. This can be attributed to the absence of UiO-66-NH2 in PSBMA/PSf membrane. As a typical MOF, UiO-66NH2 possesses a highly-ordered porous structure. Its aperture size is around 6.0 Å which is larger than the size of water molecules (~2.8 Å). Thus, UiO-66PSBMA particles in the skin layer provide additional flow paths for water permeation through their hydrophilic porous structure as well as the tiny interspace.52,53 Besides, the existence of MOF nanoparticles among the casting solution will reduce the interaction of the polymer chains due to their inorganic constituent, thereby decreasing the compactness and density of the skin layer. The interesting porosity behavior can verify this inference to some extent. As shown in Table 2, UiO-66-PSBMA/PSf hybrid membrane shows much higher porosity value, compared to PSBMA/PSf membrane. While this may not be realized by direct incorporation of PSBMA into PSf matrix. As a result, the permeability of UiO-66-PSBMA/PSf hybrid membranes is also much higher than that of PSBMA/PSf membrane. Conclusively, by the grafting of PSBMA brushes onto UiO-66-NH2, a homogeneous dispersion of UiO-66-PSBMA in the hybrid membrane can be obtained. The as-prepared UiO-66-PSBMA composite nanoparticles combine both the unique physical and chemical properties of PSBMA and the high porosity of UiO-66-NH2. As a result, the incorporation of UiO-66-PSBMA into PSf matrix not only accelerates the 22

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phase inversion during the coagulation process, endowing the hybrid membrane with highly porous structures but also helps to improve the hydrophilicity of the hybrid membrane. What’s more, the super hydrophilic MOF particles in the skin layer provide additional flow paths for water permeation through their hydrophilic porous structure as well as the tiny interspace between PSf matrix. Thus, the UiO-66-PSBMA/PSf hybrid membrane possesses a highly improved pure water flux together with a slight decrease of rejection. Compared to the membranes incorporated with UiO-66-NH2 or PSBMA, UiO-66-PSBMA/PSf membrane also shows its obvious superiority due to the well-tailored properties of UiO-66-PSBMA. 3.4 Effect of UiO-66-PSBMA loading on the membrane performance and morphologies. To gain a comprehensive insight into the influence of UiO-66-PSBMA loading on the membrane performance and morphologies, the hybrid membranes containing UiO-66-PSBMA contents from 0.1 to 1 wt% with respect to PSf content were prepared. The neat PSf membrane was also prepared for comparison. Figure 9 shows the pure water fluxes and rejections of membranes with different contents of UiO-66-PSBMA. With the increase of UiO-66-PSBMA loading, the water flux significantly increases and reaches a maximum (602 L m-2 h-1) at UiO-66-PSBMA content of 0.3wt%, which is ~2.5 times of the pristine PSf membrane (240 L m-2 h-1). The water permeability of UiO-66-PSBMA/PSf demonstrates significant advantages over most of hybrid UF membranes reported in the previous works (Table S1). But the flux no longer increases or even decreases upon addition of larger amounts of UiO-66PSBMA. At the same time, the rejection rates of these hybrid membranes decrease 23

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slightly with increasing amounts of UiO-66-PSBMA, staying at a relatively high level (> 98%). These results should be attributed to the synergetic effects between UiO-66NH2 and PSBMA.

Figure 9. Pure water flux and rejection (to BSA) of UiO-66-PSBMA/PSf hybrid membranes as a function of UiO-66-PSBMA content at 0.2 MPa operation pressure.

Figure 10. Contact angels of UiO-66-PSBMA/PSf hybrid membranes with different contents of UiO-66-PSBMA. On one hand, UiO-66-PSBMA possesses a lot of hydrophilic groups originated from zwitterionic PSBMA, thus the addition of UiO-66-PSBMA improve the hydrophilicity of membrane, and correspondingly facilitate the water molecules to pass through the membrane. To confirm the analysis above, the contact angles of hybrid 24

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membranes with different UiO-66-PSBMA loading were characterized. As shown in Figure 10, the contact angles of UiO-66-PSBMA/PSf membranes decrease as the UiO66-PSBMA loading increases, which suggests an increase in the hydrophilicity of hybrid membranes. On the other hand, the hybrid membranes obtain a more porous structure after the addition of UiO-66-PSBMA. Figure 11A shows the SEM images of cross-sections of hybrid membranes. Compared with PSf membrane, the macrovoids are suppressed and the finger-like pores turn to run through the cross-sectional structure in the hybrid membranes incorporated with 0.1 and 0.3 wt% UiO-66-PSBMA. Meanwhile, these two hybrid membranes show thinner skin layer and higher porosity, compared to other membranes (Table 3 and Figure S8). As discussed above, the hydrophilic UiO-66PSBMA can accelerate the exchange rate between solvent and non-solvent during the coagulation process, consequently leading to the creation of more porous structures.54 The existence of super hydrophilic MOF particles in the skin layer also promotes the porosity and water permeability. In addition, from Figure 11(B and C) and Table 3, the hybrid membrane incorporated with 0.3 wt% UiO-66-PSBMA exhibits the roughest surfaces. When the loading is beyond 0.3 wt%, the viscosity of the casting solution may increase, which suppresses the exchange between solvent and non-solvent.55, 56 As a result, a decrease in the surface roughness, porosity is observed as well as suppressed porous structure. These ultimately lead to a decrease in water flux.

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Figure 11. (A) The cross-sectional SEM images, (B) surface SEM images and (C) surface AFM three-dimensional surfaces of the membranes with different contents of UiO-66-PSBMA in PSf polymer. “1-6” refers to membranes with 0, 0.1, 0.3, 0.5, 0.7 and 1 wt% loading of UiO-66-PSBMA in the PSf polymer, respectively.

Table 3. Porosity, skin layer thickness, and the surface roughness values of UiO-66PSBMA/PSf membranes with different weight fractions of UiO-66-PSBMA in PSf polymer. Weight fraction of UiO66-PSBMA in PSf (%) 0 0.1 0.3 0.5 0.7 1

Porosity (%)

Skin layer thickness (nm)

Rq (nm)

Ra (nm)

63.2 68.2 73.4 65.7 64.3 62.9

241 181 164 211 245 264

11.8 14.3 19.3 18.1 13.1 11.2

9.7 11.2 15.3 15.0 10.8 8.8

3.5 Anti-fouling performance of membranes. Anti-fouling property is another important parameter for evaluating the application potential of membranes in water purification. Membrane fouling usually does harm to the membrane properties, such as flux decline, membrane degradation, and maintenance cost increasment. Thus great 26

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efforts have been devoted to improving the anti-fouling ability of membranes.57,58 In waste water, protein is one of the most common pollutants.59 Therefore, the anti-fouling performance of the pristine PSf membrane and hybrid membranes were examined through cyclic filtration using BSA as a pollutant. Figure 12A shows the time-dependent fluxes of membranes with different components. It is found that the permeation flux of the BSA solution decreased rapidly in comparison with the pure water flux at the initial stages because of protein fouling. During the filtration of BSA protein solution, the protein tends to deposit on the surfaces and be entrapped in the pores of membranes. Consequently, the pure water flux of all the membranes after cleaning could not be recovered totally to its initial value. To understand the antifouling performance more specifically, flux recovery ratio (FRR), total fouling ratio (Rt), reversible fouling ratio (Rr), and irreversible fouling ratio (Rir) values were calculated on the basis of the first circle of membrane fouling and washing.60 As shown in Figure 12 (B and C), the UiO66-PSBMA/PSf hybrid membrane shows the highest FRR of 72.5%, while this value of the pure PSf and UiO-66-NH2/PSf membranes is 64.5 and 66.9%, respectively. In addition, the reversible resistance of UiO-66-PSBMA/PSf composite membrane is 58.1%, which is higher than that of the pristine PSf membrane (45.7%) and UiO-66NH2/PSf membrane (49.5%). These results indicate that UiO-66-PSBMA/PSf hybrid membrane owns the best anti-fouling performance even though it exhibits the roughest surface. We speculate that the more hydrophilic surface of UiO-66-PSBMA/PSf hybrid membrane may attribute to the enhancement as it forms hydrated layers to inhibit protein adsorption.61 27

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Figure 12. (A) Time-dependent fluxes of membranes with different fillers during antifouling experiment with BSA filtration, (B) flux recovery ratio of test membranes and (C) fouling resistance of test membranes. Apart from the surface roughness and hydrophilicity, pH also is a significant factor which affects the BSA fouling.62 It should be noted that the pH of the feed solution used here was adjusted to 4.7 which is the isoelectric point (IEP) of BSA. The electrostatic repulsion interaction between BSA molecule and the membranes is relatively lower. Therefore, the improvement of antifouling performance here is mainly originated from the enhancement of surface hydrophilicity.63,64 What’s more, the UiO-66-PSBMA/PSf hybrid membrane presents a good stability during long-term operation. Therefore, the results suggest that the PSf membrane doped with UiO-66-PSBMA possesses an improved anti-fouling performance, showing the significant application potential in 28

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practical water purification. In fact, we believe that the overall membrane performances, including antifouling performance, can be further optimized through tailoring the chemical composition and nanostructure of UiO-66- polymer nanocomposites.65

4 CONCLUSIONS In this work, PSBMA-modified MOF nanoparticles (UiO-66-PSBMA) were firstly synthesized through a post-synthetic strategy from UiO-66-NH2. Then, it was incorporated into PSf to prepare hybrid UF membranes via a phase-inversion method. For UiO-66-PSBMA, PSBMA coating formed around MOF nanoparticles can endow UiO-66-PSBMA with super hydrophilicity. Furthermore, PSBMA coating is also helpful to the dispersion of UiO-66-PSBMA in the PSf matrix, contributing to the better compatibility of MOF nanocrystal and polymer phase. Thus it enables the design of high-performance MOF/PSf membranes for UF. The incorporation of UiO-66-PSBMA into PSf matrix results in the membrane with more hydrophilic surface and porous structure due to the unique property of UiO-66-PSBMA. What’s more, the existence of super hydrophilic MOF particles in the PSf matrix provides additional flow paths for water permeation through their hydrophilic porous structure as well as the tiny interspace between PSf matrix. Ultimately, the obtained hybrid membrane exhibits highly improved water flux and anti-fouling performance without sacrificing much of the protein retention. Therefore, the overall results highlight the promising potential of UiO-66-PSBMA in the development of UF membranes for water separation. This work provides a high-value reference for designing optimal MOF nanocomposites for water treatment membranes. 29

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ASSOCIATED CONTENT

Supporting Information. Schematic diagram of the cross-flow system during UF process; The photograph of the cross-flow cell; FESEM images of UiO-66-NH2 and UiO-66-PSBMA; Temperature-dependent turbidity of the UiO-66-PSBMA in water; Water contact angle of the UiO-66-PSBMA film; Element mapping and EDS of the surface of 0.3wt% UiO-66-PSBMA/PSf membrane; Magnified cross-sectional images of all the membranes and performance comparisons between membranes prepared in this work and previously reported UF membranes in water permeability and rejection are available as Supporting Information. This material is available free of charge via the Internet at http://pubs.acs.org. AUTHOR INFORMATION Corresponding Authors E-mail: [email protected]. Notes The authors declare no competing financial interest. ACKNOWLEDGMENT We gratefully acknowledge the financial support from the Ministry of Science & Technology of China (No. 2016YFA0203302).

REFERENCES (1) Fane, A. G.; Wang, R.; Hu, M. X. Synthetic Membranes for Water Purification: 30

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Status and Future. Angew. Chem., Int. Ed. 2015, 54, 3368-3386. (2) Shannon, M. A.; Bohn, P. W.; Elimelech, M.; Georgiadis, J. G.; Marinas, B. J.; Mayes, A. M. Science and Technology for Water Purification in the Coming Decades. Nature 2008, 452, 301-310. (3) Qu, F. S.; Liang, H.; Zhou, J.; Nan, J.; Shao, S. L.; Zhang, J. Q.; Li, G. B. Ultrafiltration Membrane Fouling Caused by Extracellular Organic Matter (EOM) from Microcystis Aeruginosa: Effects of Membrane Pore Size and Surface Hydrophobicity. J. Membr. Sci. 2014, 449, 58-66. (4) Wu, H. Q.; Tang, B. B.; Wu, P. Y. Development of Novel SiO2-GO Nanohybrid/Polysulfone Membrane with Enhanced Performance. J. Membr. Sci. 2014, 451, 94-102. (5) Yang, L. J.; Tang, B. B.; Wu, P. Y. UF Membrane with Highly Improved Flux by Hydrophilic Network between Graphene Oxide and Brominated Poly(2,6-dimethyl1,4-phenylene oxide). J. Mater. Chem. A 2014, 2, 18562-18573. (6) Lee, S. J.; Dilaver, M.; Park, P. K.; Kim, J. H. Comparative Analysis of Fouling Characteristics of Ceramic and Polymeric Microfiltration Membranes Using Filtration Models. J. Membr. Sci. 2013, 432, 97-105. (7) Zhang, Y. Q.; Liu, P. L. Polysulfone(PSF) Composite Membrane with MicroReaction Locations (MRLs) Made by Doping Sulfated TiO2 Deposited on SiO2 Nanotubes (STSNs) for Cleaning Wastewater. J. Membr. Sci. 2015, 493, 275-284. (8) Xu, Z. W.; Wu, T. F.; Shi, J.; Teng, K. Y.; Wang, W.; Ma, M. J.; Li, J.; Qian, X. M.; Li, C. Y.; Fan, J. T. Photocatalytic Antifouling PVDF Ultrafiltration Membranes 31

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Based on Synergy of Graphene Oxide and TiO2 for Water Treatment. J. Membr. Sci. 2016, 520, 281-293. (9) Damodar, R. A.; You, S. J.; Chou, H. H. Study the Self -cleaning, Antibacterial and Photocatalytic Properties of TiO2 Entrapped PVDF Membranes. J. Hazard. Mater. 2009, 172, 1321-1328. (10) Ayyaru, S.; Ahn, Y. H. Application of Sulfonic Acid Group Functionalized Graphene Oxide to Improve Hydrophilicity, Permeability, and Antifouling of PVDF Nanocomposite Ultrafiltration Membranes. J. Membr. Sci. 2017, 525, 210-219. (11) Meng, N.; Priestley, R. C. E.; Zhang, Y. Q.; Wang, H. T.; Zhang, X. W. The Effect of Reduction Degree of GO Nanosheets on Microstructure and Performance of PVDF/GO Hybrid Membranes. J. Membr. Sci. 2016, 501, 169-178. (12) Mahlangu, O. T.; Nackaerts, R.; Thwala, J. M.; Mamba, B. B.; Verliefde, A. R. D. Hydrophilic Fouling-Resistant GO-ZnO/PES Membranes for Wastewater Reclamation. J. Membr. Sci. 2017, 524, 43-55. (13) Shi, Z.; Zhang, W. B.; Zhang, F.; Liu, X.; Wang, D.; Jin, J.; Jiang, L. Ultrafast Separation of Emulsified Oil/Water Mixtures by Ultrathin Free-Standing Single-Walled Carbon Nanotube Network Films. Adv. Mater. 2013, 25, 2422-2427. (14) Zhang, J. G.; Xu, Z. W.; Mai, W.; Min, C. Y.; Zhou, B. M.; Shan, M. J.; Li, Y. L.; Yang, C. Y.; Wang, Z.; Qian, X. M. Improved Hydrophilicity, Permeability, Antifouling and Mechanical Performance of PVDF Composite Ultrafiltration Membranes Tailored by Oxidized Low-Dimensional Carbon Nanomaterials. J. Mater. Chem. A 2013, 1, 3101-3111. 32

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(15) Rowsell, J. L. C.; Yaghi, O. M. Metal-Organic Frameworks: A New Class of Porous Materials. Microporous Mesoporous Mater. 2004, 73, 3-14. (16) Furukawa, H.; Cordova, K. E.; O'Keeffe, M.; Yaghi, O. M. The Chemistry and Applications of Metal-Organic Frameworks. Science 2013, 341, 1230444. (17) Li, W. B.; Zhang, Y. F.; Li, Q. B. A.; Zhang, G. L. Metal-Organic Framework Composite Membranes: Synthesis and Separation Applications. Chem. Eng. Sci. 2015, 135, 232-257. (18) Shahid, S.; Nijmeijer, K.; Nehache, S.; Vankelecom, I.; Deratani, A.; Quemener, D. MOF-Mixed Matrix Membranes: Precise Dispersion of MOF Particles with Better Compatibility via a Particle Fusion Approach for Enhanced Gas Separation Properties. J. Membr. Sci. 2015, 492, 21-31. (19) Sorribas, S.; Gorgojo, P.; Tellez, C.; Coronas, J.; Livingston, A. G. High Flux Thin Film Nanocomposite Membranes Based on Metal-Organic Frameworks for Organic Solvent Nanofiltration. J. Am. Chem. Soc. 2013, 135, 15201-15208. (20) Wang, J.; Wang, Y. M.; Zhang, Y. T.; Uliana, A.; Zhu, J. Y.; Liu, J. D.; Van der Bruggen, B. Zeolitic Imidazolate Framework/Graphene Oxide Hybrid Nanosheets Functionalized Thin Film Nanocomposite Membrane for Enhanced Antimicrobial Performance. ACS Appl. Matel. Interfaces 2016, 8, 25508-25519. (21) Zhu, J. Y.; Qin, L. J.; Uliana, A.; Hou, J. W.; Wang, J.; Zhang, Y. T.; Li, X.; Yuan, S. S.; Li, J.; Tian, M. M.; Lin, J. Y.; Van der Bruggen, B. Elevated Performance of Thin Film Nanocomposite Membranes Enabled by Modified Hydrophilic MOFs for Nanofiltration. ACS Appl. Mater. Interfaces 2017, 9, 1975-1986. 33

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(22) Low, Z. X.; Razmjou, A.; Wang, K.; Gray, S.; Duke, M.; Wang, H. T. Effect of Addition of Two-Dimensional ZIF-L Nanoflakes on the Properties of Polyethersulfone Ultrafiltration Membrane. J. Membr. Sci. 2014, 460, 9-17. (23) Ma, J.; Guo, X. Y.; Ying, Y. P.; Liu, D. H.; Zhong, C. L. Composite Ultrafiltration Membrane Tailored by MOF@GO with Highly Improved Water Purification Performance. Chem. Eng. J. 2017, 313, 890-898. (24) Wang, C. H.; Liu, X. L.; Demir, N. K.; Chen, J. P.; Li, K. Applications of Water Stable Metal-Organic Frameworks. Chem. Soc. Rev. 2016, 45, 5107-5134. (25) Denny, M. S.; Cohen, S. M., In Situ Modification of Metal-Organic Frameworks in Mixed-Matrix Membranes. Angew. Chem., Int. Ed. 2015, 54, 9029-9032. (26) Zhu, Q. L.; Xu, Q., Metal-Organic Framework Composites. Chem. Soc. Rev. 2014, 43, 5468-5512. (27) Zhao, D.; Tan, S. W.; Yuan, D. Q.; Lu, W. G.; Rezenom, Y. H.; Jiang, H. L.; Wang, L. Q.; Zhou, H. C. Surface Functionalization of Porous Coordination Nanocages Via Click Chemistry and Their Application in Drug Delivery. Adv. Mater. 2011, 23, 9093. (28) Xie, K.; Fu, Q.; He, Y.; Kim, J.; Goh, S. J.; Nam, E.; Qiao, G. G.; Webley, P. A. Synthesis of Well Dispersed Polymer Grafted Metal-Organic Framework Nanoparticles. Chem. Commun. 2015, 51, 15566-15569. (29) Duan, J. T.; Pan, Y. C.; Pacheco, F.; Litwiller, E.; Lai, Z. P.; Pinnau, I., HighPerformance Polyamide Thin-Film-Nanocomposite Reverse Osmosis Membranes Containing Hydrophobic Zeolitic Imidazolate Framework-8. J. Membr. Sci. 2015, 476, 34

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ACS Applied Materials & Interfaces

303-310. (30) Cohen, S. M. Modifying MOFs: New Chemistry, New Materials. Chem. Sci. 2010, 1, 32-36. (31) Manos, M. J.; Kyprianidou, E. J.; Papaefstathiou, G. S.; Tasiopoulos, A. J. Insertion of Functional Groups into a Nd3+ Metal-Organic Framework via SingleCrystal-to-Single-Crystal Coordinating Solvent Exchange. Inorg. Chem. 2012, 51, 6308-6314. (32) Zhang, Y. Y.; Feng, X.; Li, H. W.; Chen, Y. F.; Zhao, J. S.; Wang, S.; Wang, L.; Wang, B. Photoinduced Postsynthetic Polymerization of a Metal-Organic Framework toward a Flexible Stand-Alone Membrane. Angew. Chem. Int. Ed. 2015, 54, 4259-4263. (33) Hou, L. M.; Wang, L.; Zhang, N.; Xie, Z. G.; Dong, D. W. Polymer Brushes on Metal-Organic Frameworks by UV-Induced Photopolymerization. Polym. Chem. 2016, 7, 5828-5834. (34) Wang, J.; Zhang, Y. T.; Zhu, J. Y.; Hou, J. W.; Liu, J. D.; Van der Bruggen, B. Zwitterionic Functionalized Layered Double Hydroxides Nanosheets for a Novel Charged Mosaic Membrane with High Salt Permeability. J. Membr. Sci. 2016, 510, 2737. (35) Fang, L. F.; Jeon, S.; Kakihana, Y.; Kakehi, J.; Zhu, B. K.; Matsuyama, H.; Zhao, S. F. Improved Antifouling Properties of Polyvinyl Chloride Blend Membranes by Novel Phosphate Based-Zwitterionic Polymer Additive. J. Membr. Sci. 2017, 528, 326-335. (36) Wang, L. J.; Su, Y. L.; Zheng, L. L.; Chen, W. J.; Jiang, Z. Y. Highly Efficient 35

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Zwitterionic

Poly(3-

(Methacryloylamino)Propyl-Dimethyl(3-Sulfopropyl) Ammonium Hydroxide). J. Membr. Sci. 2009, 340, 164-170. (37) Jiang, S. Y.; Cao, Z. Q. Ultralow-Fouling, Functionalizable, and Hydrolyzable Zwitterionic Materials and Their Derivatives for Biological Applications. Adv. Mater. 2010, 22, 920-932. (38) Wu, J.; Lin, W. F.; Wang, Z.; Chen, S. F.; Chang, Y. Investigation of the Hydration of Nonfouling Material Poly(sulfobetaine methacrylate) by Low-Field Nuclear Magnetic Resonance. Langmuir 2012, 28, 7436-7441. (39) Cavka, J. H.; Jakobsen, S.; Olsbye, U.; Guillou, N.; Lamberti, C.; Bordiga, S.; Lillerud, K. P., A new zirconium inorganic building brick forming metal organic frameworks with exceptional stability. J. Am. Chem. Soc. 2008, 130, 13850-13851. (40) Liu, X. L.; Demir, N. K.; Wu, Z. T.; Li, K., Highly Water-Stable Zirconium Metal Organic Framework UiO-66 Membranes Supported on Alumina Hollow Fibers for Desalination. J. Am. Chem. Soc. 2015, 137, 6999-7002. (41) Zhang, R.; Ji, S. L.; Wang, N. X.; Wang, L.; Zhang, G. J.; Li, J. R., Coordination-Driven In Situ Self-Assembly Strategy for the Preparation of MetalOrganic Framework Hybrid Membranes. Angew. Chem., Int. Ed. 2014, 53, 9775-9779. (42) Liu, H. Y.; Zhu, H.; Zhu, S. P. Reversibly Dispersible/Collectable MetalOrganic Frameworks Prepared by Grafting Thermally Responsive and Switchable Polymers. Macromol. Mater. Eng. 2015, 300, 191-197. (43) Song, Y.; Ye, G.; Lu, Y. X.; Chen, J.; Wang, J. C.; Matyjaszewski, K. Surface36

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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

ACS Applied Materials & Interfaces

Initiated ARGET ATRP of Poly(Glycidyl Methacrylate) from Carbon Nanotubes via Bioinspired Catechol Chemistry for Efficient Adsorption of Uranium Ions. ACS Macro Lett. 2016, 5, 382-386. (44) Tang, B. B.; Xu, T. W.; Sun, P. J.; Yang, W. H., A Novel of Positively Charged Asymmetry Membrane Prepared from Poly (2,6-Dimethyl-1,4-Phenylene Oxide) by In Situ Amination - Part III. Effect of Benzyl and Aryl Bromination Degrees of Polymer on Membrane Performance and Morphologies. J. Membr. Sci. 2006, 279, 192-199. (45) Feng, K.; Hou, L.; Tang, B. B.; Wu, P. Y., A Self-Protected Self-Cleaning Ultrafiltration Membrane by Using Polydopamine as a Free-Radical Scavenger. J. Membr. Sci. 2015, 490, 120-128. (46) Venna, S. R.; Lartey, M.; Li, T.; Spore, A.; Kumar, S.; Nulwala, H. B.; Luebke, D. R.; Rosi, N. L.; Albenze, E. Fabrication of MMMs with Improved Gas Separation Properties Using Externally-Functionalized MOF Particles. J. Mater. Chem. A 2015, 3, 5014-5022. (47) Garibay, S. J.; Cohen, S. M. Isoreticular Synthesis and Modification of Frameworks with the UiO-66 topology. Chem. Commun. 2010, 46, 7700-7702. (48) Tang, Y. P.; Chan, J. X.; Chung, T. S.; Weber, M.; Staudt, C.; Maletzko, C. Simultaneously Covalent and Ionic Bridging towards Antifouling of GO-Imbedded Nanocomposite Hollow Fiber Membranes. J. Mater. Chem. A 2015, 3, 10573-10584. (49) Lin, X. C.; Wang, K.; Feng, Y.; Liu, J. Z.; Fang, X. Y.; Xu, T. W.; Wang, H. T., Composite Ultrafiltration Membranes from Polymer and Its Quaternary Phosphonium-Functionalized Derivative with Enhanced Water Flux. J. Membr. Sci. 37

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2015, 482, 67-75. (50) Zhang, J. G.; Xu, Z. W.; Mai, W.; Min, C. Y.; Zhou, B. M.; Shan, M. J.; Li, Y. L.; Yang, C. Y.; Wang, Z.; Qian, X. M., Improved Hydrophilicity, Permeability, Antifouling and Mechanical Performance of PVDF Composite Ultrafiltration Membranes Tailored by Oxidized Low-Dimensional Carbon Nanomaterials. J. Mater. Chem. A 2013, 1, 3101-3111. (51) Le, N. L.; Quilitzsch, M.; Cheng, H.; Hong, P. Y.; Ulbricht, M.; Nunes, S. P.; Chung, T. S. Hollow Fiber Membrane Lumen Modified by Polyzwitterionic Grafting. J. Membr. Sci. 2017, 522, 1-11. (52) Trinh, D. X.; Tran, T. P. N.; Taniike, T., Fabrication of New Composite Membrane Filled with UiO-66 Nanoparticles and Its Application to Nanofiltration. Sep. Purif. Technol. 2017, 177, 249-256. (53) Xu, Y. M.; Chung, T. S., High-Performance UiO-66/Polyimide Mixed Matrix Membranes for Ethanol, Isopropanol and N-butanol Dehydration via Pervaporation. J. Membr. Sci. 2017, 531, 16-26. (54) Garcia-Ivars, J.; Iborra-Clar, M. I.; Alcaina-Miranda, M. I.; Van der Bruggen, B. Comparison between Hydrophilic and Hydrophobic Metal Nanoparticles on the Phase Separation Phenomena during Formation of Asymmetric Polyethersulphone Membranes. J. Membr. Sci. 2015, 493, 709-722. (55) Diez, B.; Roldan, N.; Martin, A.; Sotto, A.; Perdigon-Melon, J. A.; Arsuaga, J.; Rosal, R. Fouling and Biofouling Resistance of Metal-Doped Mesostructured Silica/Polyethersulfone Ultrafiltration Membranes. J. Membr. Sci. 2017, 526, 252-263. 38

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(56) Wu, H. Q.; Liu, Y. J.; Mao, L.; Jiang, C. H.; Ang, J. M.; Lu, X. H. Doping Polysulfone Ultrafiltration Membrane with TiO2-PDA Nanohybrid for Simultaneous Self-Cleaning and Self-Protection. J. Membr. Sci. 2017, 532, 20-29. (57) Shen, J. L.; Zhang, Q.; Yin, Q.; Cui, Z. L.; Li, W. X.; Xing, W. H. Fabrication and Characterization of Amphiphilic PVDF Copolymer Ultrafiltration Membrane with High Anti-fouling Property. J. Membr. Sci. 2017, 521, 95-103. (58) Xiong, S.; Zuo, J.; Ma, Y. G.; Liu, L. F.; Wu, H.; Wang, Y. Novel Thin Film Composite Forward Osmosis Membrane of Enhanced Water Flux and Anti-Fouling Property with N-3-(Trimethoxysilyl) Propyl Ethylenediamine Incorporated. J. Membr. Sci. 2016, 520, 400-414. (59) Pi, J. K.; Yang, H. C.; Wan, L. S.; Wu, J.; Xu, Z. K. Polypropylene Microfiltration Membranes Modified with TiO2 Nanoparticles for Surface Wettability and Antifouling Property. J. Membr. Sci. 2016, 500, 8-15. (60) Zhang, F.; Zhang, W. B.; Yu, Y.; Deng, B.; Li, J. Y.; Jin, J., Sol-Gel Preparation of PAA-g-PVDF/TiO2 Nanocomposite Hollow Fiber Membranes with Extremely High Water Flux and Improved Antifouling Property. J. Membr. Sci. 2013, 432, 25-32. (61) He, M. R.; Fan, X. C.; Yang, Z.; Zhang, R. N.; Liu, Y. N.; Fan, L.; Zhang, Q.; Su, Y. L.; Jiang, Z. Y. Antifouling High-Flux Membranes via Surface Segregation and Phase Separation Controlled by the Synergy of Hydrophobic and Hydrogen Bond Interactions. J. Membr. Sci. 2016, 520, 814-822. (62) Zhu, L. J.; Zhu, L. P.; Jiang, J. H.; Yi, Z.; Zhao, Y. F.; Zhu, B. K.; Xu, Y. Y., Hydrophilic and Anti-Fouling Polyethersulfone Ultrafiltration Membranes with 39

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Poly(2-Hydroxyethyl Methacrylate) Grafted Silica Nanoparticles as Additive. J. Membr. Sci. 2014, 451, 157-168; (63) Shi, Q.; Su, Y. L.; Zhu, S. P.; Li, C.; Zhao, Y. Y.; Jiang, Z. Y., A Facile Method for Synthesis of Pegylated Polyethersulfone and Its Application in Fabrication of Antifouling Ultrafiltration Membrane. J. Membr. Sci. 2007, 303, 204-212; (64) Sun, M. P.; Su, Y. L.; Mu, C. X.; Jiang, Z. Y., Improved Antifouling Property of PES Ultrafiltration Membranes Using Additive of Silica-PVP Nanocomposite. Ind. Eng. Chem. Res. 2010, 49, 790-796. (65) Song, H. J.; Jo, Y. J.; Kim, S. Y.; Lee, J.; Kim, C. K., Characteristics of ultrafiltration membranes fabricated from polysulfone and polymer-grafted silica nanoparticles: Effects of the particle size and grafted polymer on the membrane performance. J. Membr. Sci. 2014, 466, 173-182.

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