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Tailoring Membrane Surface Properties and Ultrafiltration Performances via Self-assembly of Polyethylene glycol-block-Polysulfone-blockPolyethylene glycol Block Copolymer upon Thermal and Solvent Annealing Ning Wang, Tao Wang, and Yunxia Hu ACS Appl. Mater. Interfaces, Just Accepted Manuscript • DOI: 10.1021/acsami.7b06997 • Publication Date (Web): 14 Aug 2017 Downloaded from http://pubs.acs.org on August 14, 2017
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ACS Applied Materials & Interfaces
Tailoring Membrane Surface Properties and Ultrafiltration Performances via Self-assembly of Polyethylene glycol-block-Polysulfone-block-Polyethylene glycol Block Copolymer upon Thermal and Solvent Annealing
Ning Wang,1# Tao Wang,1# and Yunxia Hu1, 2*
1. CAS Key Laboratory of Coastal Environmental Processes and Ecological Remediation; Research Center
for Coastal Environmental Engineering and Technology of Shandong Province; Yantai Institute of Coastal
Zone Research, Chinese Academy of Sciences, Yantai, Shandong Province 264003, P. R. China
2. State Key Laboratory of Separation Membranes and Membrane Processes, Tianjin Polytechnic
University, Tianjin 300387, P. R. China
# Ning Wang and Tao Wang equally contributed to this work
*Corresponding author, Tel: +86-22-83955129; E-mail:
[email protected] KEYWORDS:
Ultrafiltration,
Membrane,
Amphiphilic
block
Hydrophilicity, Antifouling.
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copolymers,
Self-assembly,
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ABSTRACT
Recently, ultrafiltration (UF) membranes faced great challenges including the fine control of the
membrane surfaces for high filtration performances and antifouling properties in treating complex
solution systems. Here, a particular type of amphiphilic block copolymers polyethylene
glycol-block-polysulfone-block-polyethylene glycol (PEG-b-PSf-b-PEG) was synthesized through
one-pot step-growth polymerization with mPEG as two ends to achieve the mobility of hydrophilic
polymer chains. Without any other polymers or additives involved, the PEG-b-PSf-b-PEG triblock
copolymer UF membrane was fabricated through the non-solvent induced phase separation (NIPS)
method. The surface properties and filtration performances of UF membranes were tailored through
the self-assembly of PEG-b-PSf-b-PEG triblock copolymers combining the thermal and solvent
annealing treatments in water at 90 oC for 16 h. The annealed PEG-b-PSf-b-PEG triblock copolymer
membrane significantly enhanced its water flux resulting from the increased mean pore size with the
improved porosity, as well as the decreased skin layer thickness, upon annealing. More importantly, the
PEG-b-PSf-b-PEG triblock copolymer membrane surface turned from hydrophobic to hydrophilic upon
annealing with the PEG enrichment on the surface, and exhibited the improved protein antifouling
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performances. Our research opens a new avenue to tailor the membrane structure and surface properties
by self-assembly of amphiphilic block copolymers upon the thermal and solvent annealing treatments.
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INTRODUCTION
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Membrane separation processes have been extensively used as an industrially practicable and
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sustainable clean technology to selectively separate and recover valuable products in various fields.1-4
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The major industrial-scale membrane separation processes include microfiltration (MF), ultrafiltration
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(UF), nanofiltration (NF), and reverse osmosis (RO), which are distinguished by their increasing fine
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separation with decreasing pore sizes in the membrane.5-8 UF membrane is a semipermeable barrier
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with pore sizes in the range of 0.1 to 0.001 micron to remove large molecules, bacteria, viruses,
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pathogens, pyrogens, fine particles, and colloidal materials.9,
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separations at low or ambient temperatures with no phase change and work as a cost-effective solution
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to have many important medical, biological, chemical, and environmental applications including
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hemodialysis, food and beverage processing, chemical and pharmaceutical manufacturing, water
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purification and wastewater reuse.11-14
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UF can produce very selective
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Now, the UF membranes are facing great challenges including the limited control of the membrane
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structure and surface properties for antifouling property and high filtration performance in treating
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complex solution systems.15,
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materials such as polysulfone (PSf), polyvinylidene difluoride (PVDF) and polyvinyl chloride (PVC)
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requires hydrophilic surface modification through blending or grafting hydrophilic materials to
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improve the filtration performances and anti-fouling properties. However, the grafting strategy suffers
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from complicate surface reaction procedures and compromises filtration performances of the
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membrane.17 The blending strategy is very simple but may deteriorate the membrane hydrophilicity
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over time due to the leaking of hydrophilic additives.18 The in situ surface segregation approach was
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reported to provide a robust and simple fouling resistant surface tailoring strategy to fabricate UF
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membranes.19-22
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polyacrylonitrile-graft-poly(ethylene oxide) (PAN-g-PEO),23, 24 polysulfone-block-poly(ethylene oxide)
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copolymers (PSf-b-PEO),25-27 Poly(vinylidene fluoride-poly(ethylene oxide)) (PVDF)-PEO) comb
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copolymers,28 and Poly(vinylidene fluoride-Polyethylene glycol dimethacrylate (PVDF-PEGMA),29
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were synthesized and blended with their hydrophobic membrane materials to cast the UF membranes
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through the non-solvent induced phase-inversion process (NIPS). The hydrophilic blocks such as PEG
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and PEGMA could segregate to polymer/water interface and thus endowed UF membranes with the
A
16
The intrinsic hydrophobicity of widely-used polymeric membrane
particular
type
of
amphiphilic
block
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copolymers,
such
as
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enhanced surface hydrophilicity for the improved fouling-resistance, and the hydrophobic block such as
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PAN, PSf, and PVDF could provide strong anchoring with the membrane skeleton to maintain
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mechanical strength.23-29 However, due to the very limited content of hydrophilic blocks in the overall
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membrane materials, the enhancement of surface hydrophilicity and filtration performances of UF
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membranes was not yet optimized through blending amphiphilic copolymer with popular membrane
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materials.25, 26
37
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Recently, to increase the hydrophilic block content in the membrane materials and surfaces, the
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amphiphilic copolymer of PSf-b-PEG was also used as the only membrane material to cast the UF
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membrane through NIPS.30 It was very interesting to find that the microphase separation of PSf-b-PEG
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block copolymers could promote the formation of the interconnected PEG microdomains and
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dramatically improve the permeability of the fabricated UF membranes.30 Although the PEG surface
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aggregation was observed on the PSf-b-PEG membrane surface, the water contact angle of the
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membrane surface was not increased much compared with the PSf membrane, which may because of
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no enough PEG enrichment on the membrane surfaces. The thermal and solvent annealing methods
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have been well-established to further promote the microphase separation of block copolymers, and
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thus to strongly drive the surface migration of one block on the thin film surfaces,31-34 which provides
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a simple and convenient approach to tailor the membrane surfaces through the directed self-assembly
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of block copolymers. To date, no work has been done to tailor the membrane structure and surface
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properties of the phase inversion polymeric membranes through the thermal or solvent annealing
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approach.
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In this work, we attempt to enhance the surface enrichment of hydrophilic polymers through the
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annealing induced self-assembly of amphiphilic block copolymers for the improved filtration and
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antifouling performances of the phase-inversion polymeric membranes. Thus, a well-defined
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amphiphilic triblock copolymer of polyethylene glycol-block-polysulfone-block-polyethylene glycol
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(PEG-b-PSf-b-PEG) was synthesized through one-pot step-growth polymerization and used as a model
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of the amphiphilic block copolymer membrane material. Without any other polymer involved, the
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non-solvent induced phase separation (NIPS) method was used to fabricate the UF membranes of
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PEG-b-PSf-b-PEG triblock copolymer. The surface properties and filtration performances of UF
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membranes were tailored through the self-assembly of PEG-b-PSf-b-PEG triblock copolymers
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combining the thermal and solvent annealing treatments in water at high temperature. X-ray
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photoelectron spectroscopy (XPS), confocal microscopy, and scanning electronic microscopy (SEM)
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were used to monitor the surface segregation process of PEG during the annealing. Membrane
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properties and performances including hydrophilicity, pure water flux, and fouling resistance to Bovine
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Serum Albumin (BSA) protein were also investigated. Our research provides a simple and effective
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approach to tailor the membrane structure and surface properties via the self-assembly of amphiphilic
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block copolymers through the thermal and solvent annealing treatments.
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2. MATERIALS AND METHODS
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2.1 Materials and Chemicals
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Bisphenol A (99 %), 4, 4’-Chlorophenyl sulfone (98 %) and N-methyl-2-pyrrolidone (NMP, 99 %)
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were purchased from Acros (New Jersey, USA). Polysulfone Udel P-3500 (PSf, Mn: 21 kg mol-1,
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measured by GPC in THF solvent) was supplied by Solvay Advanced Polymers (Alpharetta, GA,
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USA). Poly(ethylene glycol) (PEG, Mn: 150 kg mol-1, PDI 1.20 and 275 kg mol-1, PDI 1.17) was
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purchased from Polymer Source Inc. (Dorval, Quebec, Canada). Monomethylpoly(ethylene glycol)
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(mPEG, Mn: 5 kg mol-1, PDI 1.05) and bovine serum albumin (BSA, Mn : 67 kg mol-1) were
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purchased from Sigma-Aldrich (St. Louis, MO, USA). Dimethylacetamide (DMAC), toluene and
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potassium carbonate (K2CO3) were purchased from Sinopharm Chemical Reagent Co., Ltd.
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(Shanghai, China). All the materials and reagents were used as received.
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2.2 Synthesis of PEG-b-PSf-b-PEG Triblock Copolymers
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One-pot approach was adopted with a slight change from the reported method to synthesize triblock
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copolymers of PEG-b-PSf-b-PEG.35 The detailed procedure is described as follows: Bisphenol A
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(45.01 g, 0.197 mol), 4, 4’-Chlorophenyl sulfone (57.82 g, 0.201 mol), and potassium carbonate
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(82.60 g, 0.598 mol) were charged to a 1 L three-neck round-bottom flask fitted with a mechanical
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stirrer under a nitrogen atmosphere, followed by the addition of a mixture solvent of DMAC and
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toluene (500 mL DMAC, 100 mL toluene). The above reagent mixture was heated to 155 °C until
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toluene refluxed to remove a total of 10.5 mL water through the Dean-Stark trap over 3 h. The
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reaction temperature was further raised to 190 °C to promote the polymerization for 6 h, followed by
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the addition of mPEG (50.05 g, 0.01 mol, Mn: 5 kg mol-1). 2 h later, the polymerization was stopped
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upon cooling the reaction mixture to room temperature. The viscous polymer solution was precipitated
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in 2 L 0.6 M HCl aqueous solution to neutralize K2CO3. The precipitated polymer was washed
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thoroughly using water till its pH reached to 7.0. Upon filtration, the polymer was collected and dried
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in a vacuum oven at 60 °C to a constant weight.
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2.3 Characterization of PEG-b-PSf-b-PEG Triblock Copolymers
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1
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and Si(CH3)4 as an internal standard. Triblock copolymer composition was calculated from the area
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ratio of the methylene protons (4H, δ 4.16 ppm) from the mPEG blocks and the aryl protons (4H, δ
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7.80 ppm) from the PSf blocks. Gel permeation chromatography (GPC) was employed to determine
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Mn and Mw using Waters 410 GPC system equipped with two Varian PL gel 5 µm Mixed-C columns
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and RI detector, THF was used as eluent at a flow rate of 1.0 mL min-1 at 35 oC. The GPC system was
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calibrated using 12 narrow polystyrene standards from Polymer Source, Inc. (Montreal, Canada) with
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Mn ranging from 200 to 3 × 106 g mol-1. Differential scanning calorimetry (DSC) was performed on a
H NMR spectra were recorded on a Bruker 500 MHz spectrometer using Chloroform-d as the solvent
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Perkin-Elmer 7 Series Thermal Analysis System with a scan rate of 10 °C min-1 from - 50 °C to +
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250 °C. Thermal gravimetric analysis (TGA) was performed on a Mettler 5MP/PF7548/MET/400W
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instrument (Mettler Toledo Co., Switzerland) under nitrogen flow with an increased temperature rate
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of 10 °C min-1 from 200 °C to 800 °C with a purge rate of 60 mL min-1. Approximately 3 mg
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specimens were heated first from room temperature to 200 °C with 10 minutes incubation to remove
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any moisture.
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2.4 Preparation of PEG-b-PSf-b-PEG Triblock Copolymer UF Membrane
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The non-solvent induced phase separation (NIPS) method was applied to cast the UF membrane of
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PEG-b-PSf-b-PEG triblock copolymers. In a typical procedure, 12 g of PEG-b-PSf-b-PEG triblock
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copolymers was dissolved in N-methyl-2-pyrrolidone (NMP, 88 g) by stirring at 40 °C for 12 h, and
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then stored in a desiccator for 12 h to degas at room temperature. Then the solution was cast on a
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clean glass plate using a casting knife with a 250 µm gate height. The glass plate was immediately
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immersed into the precipitation water bath at 40 ± 2 oC. After 10 min in the precipitation bath, the
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casted membrane was transferred to a fresh deionized water bath for 2 h to remove the residual solvent.
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Subsequently, the fabricated membranes were annealed in deionized water at 90 oC for a period of
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time from 8 h, 12 h, 16 h, to 24 h, respectively. PSf (Udel P-3500, Mn: 21 kg mol-1, Solvay) was also
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used to prepare the membrane as controls under the same conditions as above. In addition, the dilute
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PEG-b-PSf-b-PEG triblock copolymer solution and PSf solution in NMP and in THF solvent were
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measured separately using a Malvern zetasizer (Nano ZS90, Malvern Instruments Ltd., UK).
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2.5 PEG Segregation Observation on Membrane Surface
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Confocal scanning fluorescence microscopy (CSFM, FluoView FV1000, Olympus, Japan) was used to
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investigate the surface segregation of mPEG fragment from triblock copolymers on the membrane
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surface. The mPEG could be dyed selectively with Dragendorff reagent (see supporting information),
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thus visualized at 461 nm under the excitation of 405 nm.36 To dye membrane samples, the membrane
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coupon (1 × 1 cm2) was incubated with 10 mL Dragendorff reagent (BiI3·KI) at 0.2 M HAc-NaAc
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buffer solution (pH 4.8) for 12 h, followed by a brief rinse with water. The dyed membrane coupon
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was transferred to a glass slide with a covering slide on top, and then was observed by CSFM
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(excitation: 405 nm, emission: 461 nm). All images were taken with a fixed exposure time of 1.0 s.
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2.6 Characterization of Membrane Morphology and Property
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Field emitting scanning electronic microscopy (SEM, Hitachi S-4800, Japan) was used to observe
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membrane morphologies. Cross-sectional samples were prepared by snapping the wet membranes in
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liquid nitrogen. Prior to observations, all of the samples were dried in a vacuum oven overnight and
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sputtered with 10 nm thick platinum (EMITECH SC7620 sputter coater) at the argon pressure of 0.1
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Torr. The mean pore diameter on the membrane surface and the thickness of skin layer were measured
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using the software Nano Measure based on the scale bar of SEM images. For each data, more than 50
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pores were randomly selected from the SEM images of three individual parallel specimens, and errors
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were given as the standard deviation. X-ray photoelectron spectroscopy (XPS, Thermo Escalab 250Xi,
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Thermo Fisher Scientific, USA) was employed to detect membrane surface chemistry with
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monochromatic Al Kα excitation (hν =1486.6 eV) on a spot size of 500 µm. Spectra were collected at
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60 ° takeoff angle relative to sample surface for 4 scans. The whole spectra were collected by survey
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scan from 0 ~ 1000 eV (step size: 1). High resolution scans were performed by narrow scan (step size:
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0.1) for chemical analysis of oxygen element (O, 526.0 ~ 544.0 eV). Water contact angle
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measurements were performed using the sessile drop method to study the surface hydrophilicity on an
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optical instrument (ADS300, Data physics, Germany). The dried membrane coupon (1 × 5 cm2) was
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mounted on a clean glass slide and then put on the sample holder. A deionized water droplet (2.0 µL)
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was dropped from a micro-syringe to the membrane surface, and its dynamic droplet shape was
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recorded immediately through video using the automated Drop Shape Analysis software (SCA20
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Version 2) for at least 20 minutes with 5 frames per minute. Each data point was reported as the
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average value and the standard deviation from more than 15 measurements tested on at least three
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individual parallel specimens. AFM imaging was performed using a Multimode 8 (Veeco/Digital
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Instruments, Santa Barbara, USA). Image collection and data analysis were carried out with the
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NanoScope software version 8.10, and NanoScope Analysis software version 1.10. For the roughness
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of membrane surfaces, three individual parallel specimens were measured and errors were given as the
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standard deviation.
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2.7 Membrane Porosity Measurement
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The fully-wetted membranes coupons were weighed using the electronic balance (Mettler-Toledo
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ME104E, Switzerland) after mopping superficial water with air-laid paper. The wetted membrane was
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dried in a vacuum oven at 60 °C for 24 h to achieve a constant weight before measuring the dry
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weight. Membrane porosity was determined following the reported equation (1):37
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ε = (Ww- Wd)/(ρw*V)
(1)
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Where Ww is the weight of wet membrane coupons (g), Wd is the weight of dry membrane coupons
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(g), ρ w is the density of pure water at 25 oC (g cm-3) and V is the volume of the wet membrane coupon
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(cm3). For each data point, three individual specimens were measured for parallel experiments, and
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errors were given as the standard deviation.
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2.8 Membrane Filtration and Antifouling Performances
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The membrane filtration properties were tested using a stirred filtration cell (Amicon 8010, Millipore,
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USA) following the reported protocol.38 Prior to tests, each membrane sample was pre-compacted at
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1.5 bar with DI water for 15 min, and the water flux was subsequently tested at 1.0 bar for 30 min.
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The membrane selectivity was tested using 0.1 g L-1 of PEG (Mn: 275 kg mol-1, PDI: 1.17) aqueous
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solution as the feed at 1.0 bar, and the PEG rejection was determined as (R = 1-CPermeate/CFeed). The
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PEG concentration in the permeate solution was measured using a UV-VIS spectrophotometer
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(PERSEE, TU-1810, China) as PEG was dyed with Dragendorff reagent (BiI3·KI, see supporting
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information) to have a strong absorption at 510 nm.39 The linear calibration curve was obtained
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through measuring the absorbance of the PEG and Dragendorff reagent solution at a series of PEG
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concentrations from 0, 5, 10, 15, 20, 25, 30, and 50 mg L-1, with the fixed ratio of PEG and
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Dragendorff reagent (Figure S1). All tests were taken in triplicate with separately prepared samples.
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The membrane flux (J) was calculated according to the following equation:
J=
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m ρ×S×t
(2)
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Where J (LMH bar-1, L m-2 h-1 bar-1) is the water flux, the permeate water volume over a period of
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time across the certain membrane area under the fixed pressure, m is the weight of the permeate water
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(g), ߩ is the density of water (g cm-3), S is the membrane sample area (cm-2), and t is the filtration
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time (hour), respectively. The average value of membrane flux was calculated from three individual
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specimens.
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The antifouling properties of membranes were investigated using BSA as a well-used model protein
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foulant based on the reported protocol.40 Three sequential cycles of the fouling-cleaning process were
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performed on each membrane sample simulating practical membrane filtration operations. The extents
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of water flux decline during fouling and water flux recovery after cleaning are two important
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parameters of the membrane antifouling performances. In a typical run, the membrane with the skin
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layer at the top was pre-compacted at 1.5 bar with DI water for 30 min until the flux stabilized as a
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constant. In order to keep all membranes suffer from the same amount of BSA contact with membrane
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surfaces, the initial flux of all filtration runs was set to 200 ± 10 LMH bar-1 by adjusting the applied
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pressure, and the feed solution was switched from pure water to foulant solution (15 mg L-1 BSA
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solution with 10 mM ionic strength including 9.9 mM NaCl and 0.1 mM NaHCO3), after 5 min of
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stabilization under the fixed pressure. The fouled water flux was continuously monitored for 60 min.
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Subsequently, the membrane was reversed with the skin layer facing to the bottom in the cell and
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backwashed for 30 min with 500 mL DI water filtered through under 500 rpm stirring. Then, the water
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flux of the cleaned membrane was measured with DI water at the end of one filtration cycle. All
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filtration experiments were conducted at room temperature (25 oC) under 300 rpm stirring. The
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samples were PSf UF membranes, triblock copolymer UF membranes and annealed triblock
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copolymer UF membranes in duplicate.
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2.9 BSA Absorption and Desorption on Membrane Surfaces
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An Anton Paar SurPASS electrokinetic analyzer (Anton Paar, Austria) was used to monitor the zeta
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potential change of membrane surfaces during the absorption and desorption process of BSA protein.
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All the samples were wetted with DI water, and then were assembled on the adjustable gap cell
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apparatus. The equipped Ag/AgCl electrodes were used to measure their streaming potential and the
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zeta potential data was determined using the associated software from the streaming potential slope
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versus pressure plots based on the Helmholtz-Smoluchowski approach.41 The experimental
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temperature was maintained at 25 °C. For each run, one experiment cycle included three sequential
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steps: baseline, BSA adsorption, and BSA desorption. During each step, the zeta potential of each
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membrane sample was measured and recorded with running time using different background
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electrolyte solutions, till reached to a plateau after 600 s. For both baseline and BSA desorption
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measurement, the background electrolyte was 1 µM phosphate buffered saline (PBS, pH 7.2 ~ 7.4).
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For BSA adsorption step, the background electrolyte was 0.5 g L-1 BSA in 1 µM PBS solution. All the
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measurements were at 300 mbar.
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3. RESULTS AND DISCUSSION
227
3.1 Synthesis and Characterization of PEG-b-PSf-b-PEG Triblock Copolymers
228
The PEG-b-PSf-b-PEG triblock copolymers have been demonstrated to be synthesized through the
229
nucleophilic substitution polymerization at a weak base when monomethyl poly(ethylene glycol)
230
(mPEG) was used as an end-capping reagent to react with chloro-terminated polysulfone.42
231
Polymerization stoichiometry was manipulated to ensure PSf with chlorine as end groups using a little
232
excessive 4, 4’-Chlorophenyl sulfone monomer during the condensation polymerization of 4,
233
4’-Chlorophenyl sulfone and Bisphenol A.26 As shown in Figure 1A, the one-pot approach was
234
applied to synthesize the chloro-terminated polysulfone first, followed by the in situ addition of mPEG
235
to obtain the PEG-b-PSf-b-PEG triblock copolymers. GPC was employed to measure the
236
time-dependent molecular weight change of the synthesized polysulfone. Figure 1B shows that the
237
number-average molecular weight of the synthesized polysulfone increased significantly from 2.5 ×
238
103 g mol-1 to 1.9 × 104 g mol-1 with the prolonged polymerization time from 1 h to 6 h. Further
239
prolonging reaction time to 12 h, the molecular weight of polysulfone did not change much compared
240
with the obtained polysulfone at 6 h, suggesting the polymerization of Bisphenol A and 4,
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4’-chlorophenyl sulfone completed in 6 h.35
A
O
CH3 C CH3
HO
OH
O Cl
O
S O
+
Cl
Cl
S O DMAc/Toluene K2CO3 155-190 oC O
CH3 C CH3
O
S O
n
Cl
H3C OCH2CH2 OH m 190 oC
O CH3O CH2CH2O
m
242 243
O
CH3 C CH3
O
S O
B
O n
S O
O CH2CH2 OCH2CH2 OCH3 m
C 1h 3h 6h 12 h
15
244 245
16
17
18
19
20
21
Retention time (min)
246
Figure 1. Synthesis and characterization of PEG-b-PSf-b-PEG triblock copolymer: (A) Synthesis scheme of
247
PEG-b-PSf-b-PEG triblock copolymer; (B) GPC traces of chloro-terminated polysulfone (Cl-PSf-Cl) products upon 1 h,
248
3 h, 6 h and 12 h polymerizations, respectively; (C) 1H NMR spectrum of PEG-b-PSf-b-PEG triblock copolymer. The
249
insets display the triplet peak at 4.16 ppm from the methylene protons of mPEG and the peak at 6.76 ppm from the aryl
250
protons at terminal 4, 4’-Chlorophenyl sulfone unit of the achieved product after the certain time of nucleophilic
251
substitution polymerization between Cl-PSf-Cl and mPEG varying from 0.5 h (①), 1 h (②), 1.5 h (③), to 2 h (④).
252
(Solvent: Chloroform-d, Temperature: 25 oC).
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Upon the complete polycondensation of Bisphenol A and 4, 4’-Chlorophenyl sulfone at 190 oC for 6 h,
254
mPEG was added as the end-capping reagent. 1H NMR was employed to monitor the nucleophilic
255
substitution of Cl-PSf-Cl with the hydroxyl groups of mPEG. The triplet peaks at 4.16 ppm from the
256
methylene protons of mPEG (4H, denoted as h in the polymer backbone shown in Figure 1C)
257
increasingly grew big with the prolonged reaction time from 0.5 h, 1.0 h, 1.5 h, to 2 h, indicating the
258
increasing mPEG was linked with PSf backbone (Figure 1C). Meanwhile, the peak at 6.76 ppm (4H,
259
denoted as g in Figure 1C) from the aryl protons at terminal 4, 4’-Chlorophenyl sulfone unit kept
260
constant as a marker even with the increased reaction time since the number of PSf chains did not
261
change any more with time once synthesis.26 The integrated area ratio of aryl protons at 6.76 ppm
262
from the PSf and methylene protons at 4.16 ppm from PEG was used as an indicator to determine the
263
incorporation of PEG into the PSf backbone, which should be 1.0 as the PEG worked as an
264
end-capping reagent to terminate both ends of the PSf backbone.43 With the prolonged reaction time
265
from 0.5 h to 2 h, the integrated area ratio of aryl protons from the PSf and methylene protons from
266
PEG remarkably decreased from 11.8 to 1.0, suggesting that the reaction of mPEG and Cl-PSf-Cl
267
completed within 2 h (Figure 1C inset). In addition, from 1H NMR analysis, the weight percentage of
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268
mPEG in the PEG-b-PSf-b-PEG triblock copolymer was 28.5 wt. % based on the molecular weight of
269
PEG and PSf in the copolymer.44
270
271
To characterize the final product of PEG-b-PSf-b-PEG triblock copolymer, GPC, DSC, and TGA
272
were used to analyze its molecular weight, glass transition temperature, and the thermal
273
decomposition behavior, respectively. GPC results show that apparent molecular weight of the
274
synthesized PEG-b-PSf-b-PEG triblock copolymer was 1.6 × 104 g mol-1 with a relatively narrow
275
polydispersity index (PDI) 2.05 (Figure 2A). However, compared with the Mn of the intermediate
276
product Cl-PSf-Cl as 1.9 × 104 g mol-1, the apparent molecular weight of the final product
277
PEG-b-PSf-b-PEG triblock copolymer did not increase, which may due to the PEG incorporation in
278
the triblock copolymer increasing its solubility in THF solvent based on the like-dissolves-like
279
principle (Hansen solubility parameters of PSf, PEG, and THF are 22.9 MPa1/2, 21.6 MPa1/2, and
280
19.4 MPa1/2, respectively).43, 45 In addition, the size of PEG-b-PSf-b-PEG triblock copolymer was 5
281
nm in diameter in THF, measured through the scattering method using the Malvern zetasizer (Nano
282
ZS90), which was much smaller than the size of Cl-PSf-Cl as 10 nm in diameter in THF (Figure S3).
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Furthermore, different from the blending of PEG and PSf having their individual Tg peaks, the
284
PEG-b-PSf-b-PEG triblock copolymer has only one Tg peak, which further confirms that the PEG
285
block and PSf block are covalently bonded together, and the synthesized PEG-b-PSf-b-PEG triblock
286
copolymer has high purity without free PEG in the product. In addition, the PEG incorporation in the
287
PEG-b-PSf-b-PEG triblock copolymers significantly decreased its glass transition temperature (Tg) to
288
133.8 oC, compared with the Tg of Cl-PSf-Cl as 192.4 oC and the melt point of PEG as 66.6 oC
289
(Figure 2B), which confirms that the successful PEG incorporation in the triblock copolymer lowered
290
the temperature where polymer chain can move.43 Moreover, the PEG-b-PSf-b-PEG triblock
291
copolymer has great thermal stability to be used as the UF membrane material, since its Tg is still far
292
higher than the working temperature of UF membranes (usually below 60 oC).
293
294
TGA results present that the degradation of PEG-b-PSf-b-PEG triblock copolymers passed through
295
two stages including the thermal decomposition of PEG blocks at a low temperature between 390 oC
296
and 485 oC, and the thermal decomposition of PSf blocks at a high temperature between 510 oC and
297
685 oC (Figure S2). The weight percentage of mPEG blocks in triblock copolymer could be
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298
calculated as 35.5 wt. % from the weight loss of PEG blocks from 390 oC to 500 oC (Table 1), which
299
was more reliable than 28.5 wt. % from the above 1H NMR analysis. Considering that the proton
300
signals in 1H NMR from PSf and PEG depend on their microenvironment in polymer chain and
301
solvent,46 the weight percentage of mPEG blocks in triblock copolymer could be underestimated. In
302
addition, the molecular weight of PEG-b-PSf-b-PEG triblock copolymer could be calculated when the
303
weight percentage of PEG was determined in the copolymer and the molecular weight of PEG was
304
measured accurately as 0.5 × 104 g mol-1 (Mn) in GPC with narrow PDI. As shown in Table 1, the Mn
305
of PEG-b-PSf-b-PEG triblock copolymer was calculated to be 3.5 × 104 g mol-1 when the weight
306
percentage of PEG was determined to be 28.5 wt. % from the 1H NMR analysis, which may
307
over-estimate the Mn of PEG-b-PSf-b-PEG triblock copolymer since the weight percentage of PEG
308
could be underestimated in 1H NMR. Moreover, from the TGA results, the weight percentage of PEG
309
was 35.5 wt. %, and the Mn of PEG-b-PSf-b-PEG triblock copolymer was calculated to be 2.8 × 104 g
310
mol-1, agreeing well with the molecular weight sum of Cl-PSf-Cl (1.9 × 104 g mol-1) and two chain
311
ends of mPEG (0.5 × 104 g mol-1) as 2.9 × 104 g mol-1 (Table 1). Above all, the PEG-b-PSf-b-PEG
312
triblock copolymer was successfully synthesized with 2.8 × 104 g mol-1 molecular weight containing
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313
35.5 wt. % of PEG.
314
315
More important, based on the synthesis scheme, a series of PEG-b-PSf-b-PEG triblock copolymers
316
with different PEG contents could be prepared through tailoring the molecular weight of
317
chloro-terminated polysulfone backbone and PEG by manipulating the monomer ratios. The
318
PEG-b-PSf-b-PEG triblock copolymer with 35.5 wt. % of PEG was selected for the membrane
319
fabrication because high PEG contents in the copolymers give us a large window to investigate how
320
the PEG-b-PSf-b-PEG triblock copolymer behaves differently from PSf during the fabrication
321
process.
322 A
C
B )
100% o
Tg=192.4 C
80% Weight (%)
Heat flow (Exo
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o
Tg=133.8 C o
Tm=66.6 C
60% 40% 20% 0%
14
16 18 20 Retention time (min)
0
50
100 150o 200 Temperature ( C)
250
400
600 o Temperature ( C)
800
323 324
Figure 2. Characterizations of various polymers including GPC traces (A), DSC curves (B), and TGA plots (C) of the
325
original homopolymer PEG (blue line), the intermediate product Cl-PSf-Cl (black line), and the final product
326
PEG-b-PSf-b-PEG triblock copolymer (red line), respectively.
327 328
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Table 1. Characterizations of PSf, mPEG, Cl-PSf-Cl, and PEG-b-PSf-b-PEG triblock copolymer. Mn
Mn
Mn
PDI
mPEG
mPEG
Tg (oC)
(g mol-1)
(g mol-1)
(g mol-1)
(GPC)
(wt. %)
(wt. %)
(DSC)
(GPC)
(1H NMR)
(TGA)
(1H NMR)
(TGA)
PSfa
2.1×104
---
---
2.17
---
---
---
mPEG
0.5×104
---
---
1.05
---
---
66.6 (Tm)
Cl-PSf-Cl
1.9×104
---
---
2.05
---
---
192.4
PEG-b-PSf-b-PEG
1.6×104
3.5×104
2.8×104
2.05
28.5
35.5
133.8
Samples
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a. Solvay Udel P-3500
331
332
3.2 PEG Segregation on the UF Membrane Surfaces through the Self-assembly of
333
PEG-b-PSf-b-PEG Triblock Copolymer upon the Thermal and Solvent Annealing
334
Upon the synthesis of the well-defined PEG-b-PSf-b-PEG triblock copolymers, the non-solvent
335
induced phase separation (NIPS) method was applied to fabricate the UF membrane of
336
PEG-b-PSf-b-PEG triblock copolymer, without any other polymers or additives involved. It has been
337
well documented that the selectivity and water permeability of the phase-inversion polymeric UF
338
membranes could be tailored through varying the concentration of polymer casting solution, and the
339
membrane pore size was generally smaller and the water permeability was lower with the higher
340
concentration of polymer casting solution.47, 48 In order to make such a UF membrane with high
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bacteria rejection and high water permeability, the optimized block copolymer concentration was 12
342
wt.% in NMP. The casting solution was clear pale yellow homogeneous solution in NMP, similar as
343
the PSf casting solution. But, the viscosity of PEG-b-PSf-b-PEG in NMP was 43 cP, much less
344
viscous than the same concentration of PSf casting solution as 121 cP. The scattering results from
345
Malvern zetasizer found the dilute PEG-b-PSf-b-PEG triblock copolymer formed micelles of 46 nm in
346
diameter in NMP solvent (Figure S4), which were much larger than 5 nm in diameter of the polymer
347
size in THF solvent. According to the Hansen solubility parameters of PSf, PEG, and NMP as 22.9
348
MPa1/2, 21.6 MPa1/2, and 22.9 MPa1/2, respectively, the micelles of PEG-b-PSf-b-PEG triblock
349
copolymer might have PSf as the shell and PEG as the core in NMP solvent.43, 45, 49
350
351
After the precipitation of the PEG-b-PSf-b-PEG triblock copolymer casting solution in coagulation
352
water bath at 40 oC, the white membrane was obtained. SEM was used to study the surface and
353
cross-section morphologies of the membranes. Figure 3 presents that the PEG-b-PSf-b-PEG triblock
354
copolymer membrane had a highly porous surface with 10 ~ 20 nm pore size in diameter and an
355
asymmetric membrane structure with a thin spongy-like skin layer and a finger-like matrix, similar as
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356
the PSf control membrane. It can be concluded that both of the PSf and PEG-b-PSf-b-PEG triblock
357
copolymers could form porous membranes without any pore-making reagent involved, at a low
358
concentration of 12 wt. % polymer casting solution. Moreover, the PSf membrane had a smooth
359
surface, but the PEG-b-PSf-b-PEG triblock copolymer membrane exhibited a clear micellar
360
morphology, which was due to the micelle formation of the PEG-b-PSf-b-PEG triblock copolymer in
361
the casting solution. The surface roughness measurement by AFM also shows that the Ra of the
362
PEG-b-PSf-b-PEG membrane is 21.5 nm, much higher than 13.4 nm of the PSf membrane, as shown in
363
Figure S6.
364
365
366
367
368
369
370
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371 PSf
PEG-b-PSf-b-PEG Mean pore diameter 12 ± 3 nm
Mean pore diameter 16 ± 4 nm
Thickness 474 ± 108 nm
Thickness 363 ± 85 nm
Surface
Mean pore diameter 11 ± 3 nm
Annealed PEG-b-PSf-b-PEG
372 Thickness 466 ± 120
nm
Cross-section
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373 374
Figure 3. SEM micrographs of the surface and cross-section morphologies of the PSf and PEG-b-PSf-b-PEG triblock
375
copolymer membranes as prepared and annealed at 90 oC in water for 16 h. The scale bars are 400 nm (top images) and
376
2 µm (bottom images) respectively.
377
378
To investigate the surface hydrophilicity of PEG-b-PSf-b-PEG triblock copolymer membranes, the
379
water contact angle of the membrane surfaces was measured to be 83.8 o against water, similar as 83.5
380
o
381
PEG-b-PSf-b-PEG triblock copolymer membrane surface had 15.6 % oxygen content, very close to
382
16.2 % oxygen content of the PSf membrane surface (Table 2). These results illustrate that the PEG
383
surface segregation was not strong enough to significantly improve the membrane surface
384
hydrophilicity during the NIPS, which agrees with the reported phenomena as not obviously
of the PSf membrane surface. The membrane surface elemental analysis by XPS found that the
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385
decreasing its water contact angle of the phase-inversion PSf-b-PEG membrane.30 Different from the
386
in situ surface segregation of hydrophilic polymers from the amphiphilic copolymers during the
387
phase-inversion membrane formation process,10,
388
PEG-b-PSf-b-PEG triblock copolymer in NMP made PSf open on the shell and made PEG squeeze
389
inside the core to minimize the entropy, and thus prevented the surface migration of PEG on the
390
membrane surfaces during the NIPS, since water could not easily and quickly pass through the PSf
391
shell to meet PEG. Thus, it needs extra energy of thermal annealing for water to meet and dissolve the
392
PEG blocks and to bring them out to the membrane surface.
26,
50,
51
the micelle formation of the
393 394
Table 2. XPS surface elemental composition analysis of the PEG-b-PSf-b-PEG triblock copolymer membranes upon
395
the annealing in water at 90 oC for a period of time. Surface elemental Oxygen area value (%)
Annealing
C-O-C/Ph-O-Ph
composition (Atomic %)
Membrane time (h)
C
O
S
Ph-O-Ph
C-O-C
S=O
PSf
0
81.0
16.2
2.9
41.4
0.0
58.6
0.0
PEG-b-PSf-b-PEG
0
82.0
15.6
2.8
30.5
28.0
41.5
0.9
8
80.3
17.2
2.5
29.6
30.4
40.0
1.0
12
79.0
18.9
2.1
29.4
30.7
39.9
1.0
16
78.2
19.8
2.0
26.0
37.9
36.1
1.5
24
81.2
16.8
2.1
27.7
33.7
38.6
1.2
396 397
The self-assembly of the PEG-b-PSf-b-PEG amphiphilic triblock copolymer was taken as a great
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398
advantage to tailor its membrane surface hydrophilicity and microstructure. The hydrophobic rigid
399
blocks of PSf and the hydrophilic flexible blocks of PEG do not like each other and phase separate on
400
a mesoscopic length scale allowing for the enrichment of PEG in its favorite thermodynamic
401
conditions.34 Combining the solvent and thermal annealing treatments of immersing the
402
PEG-b-PSf-b-PEG triblock copolymer membrane in water at 90 oC for a period of time, the membrane
403
surface hydrophilicity and chemical compositions were monitored to characterize the surface
404
segregation of PEG.
405
406
Figure 4A shows that the water contact angle of the PEG-b-PSf-b-PEG triblock copolymer membrane
407
surface dropped down significantly from 83.8 o to 30.0 o with the prolonged annealing time from 0 h to
408
16 h, illustrating that the PEG-b-PSf-b-PEG triblock copolymer membrane surface achieved the
409
increasing hydrophilicity upon the annealing treatments. The membrane surface elemental
410
composition shown in Table 2 presents that the element oxygen content increased from 15.6 % to
411
19.8 %, and the element sulfur content decreased from 2.8 % to 2.0 %, correspondingly, suggesting
412
that the increasing PEG amount was observed on membrane surface. To fit the O1s peak into Ph-O-Ph
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413
at 533.1 eV, C-O-C at 532.3 eV, and S=O at 531.6 eV,44 the peak of C-O-C from PEG segments on the
414
membrane surface grew bigger, and its area percentage increased from 28.0 %, 30.4 %, 30.7 % to
415
37.9 % with the prolonged annealing time from 0 h, 8 h, 12 h, to 16 h (Figure 5). Meanwhile, the ratio
416
of C-O-C/Ph-O-Ph also increased from 0.9, 1.0, 1.0 to 1.5, correspondingly, on the PEG-b-PSf-b-PEG
417
triblock copolymer membrane surface upon the annealing treatments, further confirming the
418
increasing PEG enrichment upon the increasing annealing time. Interestingly, after correlating the
419
water contact angles and the surface elements on the PEG-b-PSf-b-PEG triblock copolymer
420
membrane surface (shown in Figure 4B), it was found that the water contact angles of the membrane
421
surface decreased with the increase of PEG enrichment on the membrane surface, further proving that
422
the improved hydrophilicity was attributed to the increased PEG on the membrane surface. All these
423
results conclude that the surface segregation and enrichment of PEG occurred and the membrane
424
surface hydrophilicity could be tailored upon the annealing treatments. However, further prolonging
425
the annealing time to 24 h, the area percentage of C-O-C decreased down to 33.7 %, the ratio of
426
C-O-C/Ph-O-Ph also dropped to 1.2, and the water contact angle of the membrane surface increased
427
up to 50.0 o, suggesting less PEG and more PSf was present on the membrane surface with the
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428
ACS Applied Materials & Interfaces
improved hydrophobicity.
429
430
It is very interesting to find that the PEG surface segregation and membrane surface hydrophilicity
431
was greatly dependent on the annealing time. The annealing condition of cooking membrane at 90 °C
432
water is favor for PEG to activate and to migrate since water is a good solvent of PEG and 90 °C is
433
high above the Tg of PEG, but not for PSf. For the pristine PEG-b-PSf-b-PEG triblock copolymer
434
membrane, PSf dominated on the membrane surface as micelles and PEG was squeezed inside the
435
micelles to minimize the entropy. It was difficult for water to diffuse through PSf and to dissolve PEG
436
in the micelles. Thus, it took quite long time and high temperature for water to penetrate the PSf shell
437
to meet PEG, and the initial stage was generally long for most of the block copolymer films under the
438
thermal annealing.52 Once PEG solubilized in water and gained extra energy to move, it could reverse
439
the micelles with PEG on the shell and PSf on the core to significantly improve the membrane surface
440
hydrophilicity. Two chain ends of PEG in the PEG-b-PSf-b-PEG triblock copolymer give PEG
441
freedom to migrate on the membrane surface, while, they could drag PSf to move passively due to the
442
chemical bonds of PEG and PSf.34
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443
Thus, under the equilibrium state, all PEG blocks microphase separated from PSf blocks and stayed in
444
a favorable membrane surface to squeeze PSf underneath the surface in a lamellar structure and to
445
minimize the entropy. While, excess energy was given to break the thermodynamic equilibrium of the
446
PEG and PSf, all PEG loved to move on the membrane surface with dragging PSf to move on the
447
surface and breaking their ideal lamellar structure. Generally, the equilibrium state is quite fragile and
448
easy to break. The membrane after 16 h annealing treatment might be close to the equilibrium state of
449
the microphase separation of PEG-b-PSf-b-PEG triblock copolymer. For 12 h annealing treatment, the
450
membrane surface has limited PEG enrichment to improve its hydrophilicity. But for 24 h annealing
451
treatment, PSf block would be dragged to move towards the membrane surface passively when two
452
ends of PEG had excess energy and driving force to enrich on the membrane surfaces under the
453
overcooked excess annealing conditions. Thus, the surface movement of PSf was observed on the
454
membrane surface when the annealing time was 24 h even at 90 oC lower than its Tg.
455
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A
B 1.6
C-O-C to Ph-O-Ph Ratio
100
o
Water contact angle ( )
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80 60 40 20 0 0h
8h
12h
16h
24h
1.4 1.2 1.0 0.8 0.6
Annealing time (h)
100
80
60
40
20
0
o
Water contact angle ( )
456 457
Figure 4. (A) Water contact angles of the PEG-b-PSf-b-PEG triblock copolymer membranes upon the annealing in
458
water at 90 oC for 0 h, 8 h, 12 h, 16 h and 24 h, respectively. The water droplets on the membrane surface were imaged
459
upon touching the membrane surfaces for 40 s. (B) The C-O-C to Ph-O-Ph ratio versus water contact angles of the
460
annealed PEG-b-PSf-b-PEG triblock copolymer membrane surfaces.
461 462 463 464 465 466 467 468 469 470 471 472 473 474 475 476 477 478
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479 PSf
Ph-O-Ph, 533.1 eV
S=O, 531.6 eV Area (%) 58.6
Area (%) 41.4
480
540
538
536
534
532
PEG-b-PSf-b-PEG, Annealed 0 h
530
528
526
C-O-C, 532.3 eV
Area (%) 30.5
Area (%) 28.0
Area (%) 29.6
Area (%) 30.4
Area (%) 29.4
Area (%) 30.7
Area (%) 26.0
Area (%) 37.9
Area (%) 27.7
Area (%) 33.7
481 Annealed 8 h
482 Annealed 12 h
483 Annealed 16 h
484 Annealed 24 h
485 486 487
540
538
536
534
532
530
528
526
488
Figure 5. The O1s XPS spectra of PEG-b-PSf-b-PEG triblock copolymer membrane surface upon annealing in water at
489
90 oC for 0 h, 8 h, 12 h, 16 h, and 24 h, respectively.
Binding Energy (eV)
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490
To directly visualize the PEG surface enrichment on the membrane surface, the Dragendorff reagent
491
was used to selectively stain the PEG blocks on the membrane surface and was visualized at 461 nm
492
under the excitation of 405 nm using CSFM.36 Confocal images shown in Figure 6 found that no
493
fluorescence was observed on the PSf membrane, but a well-distributed green fluorescence was
494
observed all over on the PEG-b-PSf-b-PEG triblock copolymer membrane surface, and the green
495
fluorescence from the stained PEG blocks was much stronger for the annealed membrane surface
496
upon 16 h annealing in water at 90 °C than the pristine triblock copolymer membrane due to the
497
thermal and solvent induced self-assembly of block copolymers.52 These confocal results clearly
498
demonstrate the surface segregation and the enrichment of PEG blocks upon annealing.
499 PSf
PEG-b-PSf-b-PEG
Annealed PEG-b-PSf-b-PEG
500 501 502 503 504 505 506
Figure 6. Confocal scanning fluorescence images of the PSf and PEG-b-PSf-b-PEG triblock copolymer membrane
507
before and after 16 h annealing in water at 90 °C. The samples were stained with the Dragendorff reagent and then
508
visualized under the excitation of 405 nm and the emission of 461 nm. The scale bars are 100 µm.
509
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510
3.3 Filtration Properties of PEG-b-PSf-b-PEG Triblock Copolymer Membrane upon Annealing
511
To investigate the influence of annealing on the membrane properties and filtration performances, the
512
water flux and rejection of the PSf and PEG-b-PSf-b-PEG triblock copolymer membrane were
513
measured before and after the same annealing conditions as cooking membranes in water at 90 °C for
514
16 h. For the PSf membrane, the annealing treatment did not change its water flux much, but
515
decreased its PEG rejection from 87.6 ± 1.0 % to 83.1 ± 2.0 % as shown in Table 3. Interestingly, the
516
annealing treatment dramatically changed the filtration performances of the PEG-b-PSf-b-PEG
517
triblock copolymer membrane with improving its water flux by 194.8 % from 397 ± 5 LMH bar to
518
1231 ± 115 LMH bar, and decreasing its PEG275kDa rejection by 5.6 % from 83.3 ± 1.0 % to 77.7 ±
519
3.4 %, compared with the pristine triblock copolymer membrane before annealing. The annealing
520
process slightly increased its surface pore size from 12 ± 3 nm to 16 ± 4 nm in diameter, improved its
521
porosity from 85.2 ± 1.3 % to 87.1 ± 0.5 %, and relatively decreased its top skin layer thickness from
522
474 ± 108 nm to 363 ± 85 nm for the PEG-b-PSf-b-PEG triblock copolymer membrane. Therefore, it
523
was a good advantage for the thermal and solvent annealing treatment to improve the membrane
524
surface hydrophilicity and filtration performances simultaneously. The tailored UF membrane with
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525
high flux and super hydrophilicity can be used for the concentration of the fermentation broth, which
526
is shown in Figure S5. In addition, the annealed PEG-b-PSf-b-PEG triblock copolymer membrane
527
demonstrated to present good mechanical strength withstanding the pressure of 0.3 MPa under the
528
dead-end filtration operation and the shear stress under the cross-flow of the UF operation.
529
530
It has been reported that the self-assembly of amphiphilic block copolymers could be induced through
531
solvent or thermal annealing where one of the blocks improved its chain mobility and phase separated
532
from the other blocks.53, 54 Under the annealing condition, water is a good solvent for PEG blocks but
533
a non-solvent for PSf blocks, and 90 °C is far higher than the Tm of PEG blocks (66.6 °C) but lower
534
than the Tg of PSf blocks (192.4 °C, Table 1). Thus, the PEG chains locally solubilized in water and
535
achieved their mobility to assemble at the interface of water/membrane pore, leading to the PEG
536
enriched on the membrane surface and the pore surface. Meanwhile, the chemical bonding with PEG
537
chains and the conformational entropy loss of the unlike blocks drove the PSf chains squeeze
538
underneath the PEG layer, like lamellar structure with PEG on top (shown in TOC). Furthermore,
539
upon the evaporation of water in the following air dry process at room temperature, the PEG chains
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540
dehydrated and shrank, leading to the increase of pore size, and the thinning of the skin layer, but PSf
541
chains lost their mobility and squeezed in the membrane skeleton. Both the surface elemental analysis
542
by XPS and surface hydrophilicity characterization by contact angle measurement had confirmed that
543
PEG was assembled and enriched on the membrane surface upon the annealing, suggesting the surface
544
rearrangement of PEG and PSf. Moreover, PEG is also known as a pore-making agent, and its
545
mobility could cause the rearrangement of PEG and PSf chains to release the free volume and thus
546
produce pores, effectively increasing the porosity of the PEG-b-PSf-b-PEG triblock copolymer
547
membrane.25, 34 Above all, the self-assembly of PEG-b-PSf-b-PEG triblock copolymers provided a
548
simple and unique way to tailor the membrane surface structure and properties upon the annealing
549
process in water at high temperature. Compared with other popular surface modification strategies, the
550
PEG surface enrichment was expected to occur homogeneously at both external and internal pore
551
surfaces (three-dimensional surfaces) through this unique self-assembly process. The covalent linkage
552
between the hydrophilic blocks PEG and the hydrophobic membrane forming blocks PSf gives
553
another key advantage of preserving the membrane surface integrity during use and avoiding the
554
leaking of additives to the permeate and thus to induce the associated toxicity issues.
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555
Table 3. The annealing influences on pure water flux (PWF), porosity, mean pore size, skin layer thickness, and PEG
556
rejection of the PSf and PEG-b-PSf-b-PEG triblock copolymer membranes. Annealing condition: in water at 90 °C for
557
16 h. PWF
Rejection
Average Pore
Skin layer
Porosity
(LMH bar)
(%)a
Diameter
Thickness
(%)
(nm)
(nm)
Membrane
PSf
344 ± 23
87.6 ± 1.0
11 ± 3
466 ± 120
83.0 ± 1.2
Annealed PSf
328 ± 12
83.1 ± 2.0
11 ± 3
472 ± 113
82.9 ± 0.5
PEG-b-PSf-b-PEG
397 ± 5
83.3 ± 1.0
12 ± 3
474 ± 108
85.2 ± 1.3
Annealed
1231 ± 115
77.7 ± 3.4
16 ± 4
363 ± 85
87.1 ± 0.5
PEG-b-PSf-b-PEG
558
a.
559
3.4 Antifouling Performances of the PEG-b-PSf-b-PEG Triblock Copolymer Membrane
560
PEG segregation on the membrane surface could endow the PEG-b-PSf-b-PEG triblock copolymer
561
membrane with excellent hydrophilicity and provide a hydration layer acting as a repulsive barrier to
562
foulant with great potential to achieve the antifouling performance.16 In the current study, the fouling
563
behavior of the annealed PEG-b-PSf-b-PEG triblock copolymer membrane was systematically
564
investigated through the surface zeta potential monitoring upon the absorption and desorption of
565
protein and also through the flux monitoring during filtration runs using a model protein foulant BSA.
566
Dynamic adsorption and desorption process of model protein BSA on the membrane surface was
567
investigated to determine whether the PEG enriched membrane surface could have antifouling
275 kDa PEG Rejection.
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568
properties towards the protein. The zeta potential of the membrane surface was monitored upon the
569
adsorption and desorption of BSA. The results shown in Figure 7 found that all three different
570
membranes shared the similar trends of their zeta potential increasing upon the absorption of BSA,
571
and decreasing after the desorption of BSA. It is easy to understand that the membrane surfaces were
572
covered with BSA upon its absorption and their surface zeta potential increase was attributed to the
573
accumulated BSA since BSA had the zeta potential of -10.6 mV in PBS solution, higher than all of the
574
three membrane surfaces. Furthermore, the membrane surface with the excellent protein antifouling
575
performance could recover to its pristine state and recover its original zeta potential if the absorbed
576
BSA could be washed out and removed completely during the desorption process.41 Figure 7 presents
577
that the annealed PEG-b-PSf-b-PEG triblock copolymer membrane surface could recover 90.3 % of
578
zeta potential from -19.5 mV to its original value of -20.0 mV after the BSA absorption and
579
desorption process, exhibiting much better zeta potential recovery than 46.0 % of the pristine
580
PEG-b-PSf-b-PEG triblock copolymer membrane without PEG enrichment on surface from -19.3 mV
581
to its original value of -24.9 mV. Thus, it can be concluded that the annealed PEG-b-PSf-b-PEG
582
triblock copolymer membrane surface greatly improved the protein antifouling performance once PEG
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583
was enriched on the membrane surface. However, the pristine PEG-b-PSf-b-PEG triblock copolymer
584
membrane showed a worse zeta potential recovery than 65.3 % of the PSf membrane, which may be
585
due to the observed rough micellar surface, shown in Figure 3 and Figure S6.
586 PSf
PEG-b-PSf-b-PEG
Adsorption
Baseline
Desorption
Adsorption
Baseline
-10
Annealed PEG-b-PSf-b-PEG
Desorption
-30
0
600
587
1200
-15 -20 5.6 mV -25 -30
-20 0.5 mV
-30
-35
1800
0
Time (s)
Sample
Desorption
-10
Zeta Potential (mV)
1.7 mV
-20
Adsorption
Baseline
-10
Zeta Potential (mV)
Zeta Potential (mV)
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
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600
1200
1800
0
Time (s)
600
1200
1800
Time (s)
Baseline
Adsorption
Desorption
Recovery
(mV)
(mV)
(mV)
percentage (%)
PSf
-19.2
-14.2
-17.5
66.0
PEG-b-PSf-b-PEG
-24.9
-14.6
-19.3
45.6
Annealed
-20.0
-14.8
-19.5
90.4
PEG-b-PSf-b-PEG
588
Figure 7. The zeta potential change of the PSf membranes, pristine PEG-b-PSf-b-PEG triblock copolymer membranes,
589
and annealed PEG-b-PSf-b-PEG triblock copolymer membranes upon the absorption and desorption of BSA on the
590
membrane surfaces. For both of the baseline and BSA desorption measurements, the background electrolyte was 1 mM
591
PBS (pH 7.2 ~ 7.4). For the BSA adsorption step, the background electrolyte was 1 g L-1 BSA in 1 mM PBS solution.
592
The annealed condition: in water at 90 °C for 16 h.
593 594
To study the protein fouling effect on the membrane filtration performance, the water flux was
595
monitored in the dead-end filtration process with 15 mg L-1 BSA solution in 10 mM ionic strength
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596
(9.9 mM NaCl and 0.1 mM NaHCO3) as the feed. For all filtration runs, an initial flux of 200 LMH
597
bar-1 was maintained through the adjusted operating pressure to ensure an equitable comparison of
598
antifouling property for all different membranes,55 and the rigorous stirring (500 rpm) near the
599
membrane surface was carried out to minimize the concentration polarization of BSA.56 Therefore, the
600
flux decline was mainly caused by protein fouling. Physical cleaning was performed to remove the
601
protein foulants through backwashing the membrane with skin layer facing to the bottom in the cell,
602
and the recovered flux was attributed to the reversible fouling (Rr), and the non-recovered flux was
603
recognized as irreversible fouling (Rir). Figure 8 presents that all three different membranes suffered
604
their flux decline upon the deposition of BSA, and recovered their flux partially upon the physical
605
cleaning of removing BSA in the tested three cycles. For example, the pristine PEG-b-PSf-b-PEG
606
membrane and PSf membrane suffered an instant rapid flux decline in 20 minutes to 58.7 % and 58.9 %
607
of their initial flux due to instant fouling, and then linearly decreased water flux to 51.3 % and 39.7 %
608
of their initial flux at the end of the fouling cycle, respectively, where the flux still exhibited a
609
decreasing tendency. After the backwashing operation, the pristine PEG-b-PSf-b-PEG triblock
610
copolymer membrane and PSf membrane achieved only a slight increase of Rr (72.9 % and 74.3 %)
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611
and the Rir (27.1 % and 25.7 %), indicating their poor antifouling property. In addition, the pristine
612
PEG-b-PSf-b-PEG triblock copolymer membrane did exhibit weaker fouling resistance than the PSf
613
homopolymer membranes due to its rough micellar surface morphology. The AFM images shown in
614
Figure S6 illustrate that the surface roughness of PEG-b-PSf-b-PEG triblock copolymer membrane is
615
21.5 nm (Ra), much higher than 13.4 nm of PSf membrane. In a sharp contrast, the annealed
616
PEG-b-PSf-b-PEG triblock copolymer membrane maintained 95.0 % of the initial flux after the instant
617
flux decline, then soon attained a plateau at 61.7 % as BSA foulant accumulated on the membrane
618
surface, and recovered more than 86.4 % of the initial water flux with only 13.6 % of Rir upon the one
619
cycle backwashing operation, demonstrating the enhanced antifouling property of the annealed
620
PEG-b-PSf-b-PEG triblock copolymer membrane. Moreover, this high water flux recovery (71.1 %
621
and 70.8 %, Figure 8) was consistently obtained in the further two filtration cycles, suggesting the
622
antifouling characteristics of the annealed PEG-b-PSf-b-PEG triblock copolymer membrane were
623
greatly improved once PEG was enriched on the three-dimensional membrane surfaces and pore
624
walls.
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PSf
PEG-b-PSf-b-PEG
100
Cycle-3
Cycle-2
Cycle-1
Normalized Flux (%)
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Annealed PEG-b-PSf-b-PEG
Rinse Rinse
Rinse
80
60
40 0
50
100
150
200
250
Time (min)
625 Cycle
Reversible fouling (%) PSf
PEG-b-PSf-b-PEG
Irreversible fouling (%) Annealed
PSf
PEG-b-PSf-b-PEG
PEG-b-PSf-b-PEG
Annealed PEG-b-PSf-b-PEG
I
74.3
72.9
86.4
25.7
27.1
13.6
II
64.8
57.9
71.1
35.2
42.1
28.9
III
62.4
55.3
70.8
37.6
44.3
29.2
626
Figure 8. The flux decline of the PSf membranes, pristine PEG-b-PSf-b-PEG triblock copolymer membranes, and
627
annealed PEG-b-PSf-b-PEG triblock copolymer membranes with time upon BSA fouling in the three sequential
628
dead-end filtration cycles. The filtration operation included three steps and three cycles: pure water permeation, BSA
629
solution filtration (15 mg L-1 BSA solution with 10 mM ionic strength including 9.9 mM NaCl and 0.1 mM NaHCO3),
630
and backwashing of the membranes with 500 mL DI water filtered through under 500 rpm stirring for 30 min. The
631
recovery water flux (Jr) was measured to determine the reversible fouling (Rr) using the following equation: Rr=(Jr/Jo)
632
×100 %, where J0 is the initial pure water flux. The initial flux of all the membranes is 200 LMH bar, and the
633
normalized flux was defined as the relative percentage of real-time flux to the initial pure water flux (J/J0).
634
Experimental conditions for all filtration cycles were 500 rpm stirring at room temperature (25 ± 1 °C). The annealing
635
condition: in water at 90 °C for 16 h.
636
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637
4. CONCLUSIONS
638
In conclusion, a particular type of PEG-b-PSf-b-PEG amphiphilic block copolymers was synthesized
639
with mPEG as two ends to achieve the mobility of hydrophilic polymer chains. Without any other
640
polymer or additive involved, the UF membranes of PEG-b-PSf-b-PEG triblock copolymer was
641
fabricated through NIPS. The thermal and solvent annealing treatments in water at 90 °C for 16 h was
642
performed to induce the microphase separation of PEG-b-PSf-b-PEG amphiphilic triblock copolymers
643
and to direct the PEG surface segregation on the membrane surfaces. The annealed PEG-b-PSf-b-PEG
644
triblock copolymer membrane significantly enhanced its water flux resulting from the increased mean
645
pore size with the improved porosity, as well as the decreased skin layer thickness, upon annealing.
646
More importantly, the PEG-b-PSf-b-PEG triblock copolymer membrane surface turned from
647
hydrophobic to hydrophilic upon annealing with PEG enrichment on the surface, and exhibited the
648
improved protein antifouling performances. Our research opens a new avenue to fabricate high
649
performance UF membranes using amphiphilic block copolymers and to tailor their pore structure and
650
surface properties through a simple and effective annealing treatment.
651
652
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653
ACKNOWLEDGMENTS
654
The authors gratefully acknowledge the funding support from National Natural Science Foundation of
655
China (No. 21476249), Key Science and Technology Program of Shandong Province (No.
656
2014GHY115021), and Key Science and Technology Program of Yantai City (No. 2015ZH063).
657
ASSOCIATED CONTENT
658
Supporting Information
659
Preparation of the Dragendorff reagent, derivative thermogravimetry curves of Cl-PSf-Cl, mPEG and
660
PEG-b-PSf-b-PEG triblock copolymers, the size of Cl-PSf-Cl and PEG-b-PSf-b-PEG triblock
661
copolymers in THF and NMP solvent. This material is available free of charge via the Internet at
662
http://pubs.acs.org.
663
AUTHOR INFORMATION
664
Corresponding Authors
665
*Yunxia Hu, E-mail:
[email protected].
666
Author Contributions
667
All authors have given approval to the final version of the manuscript. Ning Wang and
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668
Tao Wang contributed equally to this work.
669
Notes
670
The authors declare no competing financial interest.
671 672
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Ismail, A., Membrane Technology Enhancement in Oil-water Separation. A Review. Desalination
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