Skip to main content

Thank you for visiting You are using a browser version with limited support for CSS. To obtain the best experience, we recommend you use a more up to date browser (or turn off compatibility mode in Internet Explorer). In the meantime, to ensure continued support, we are displaying the site without styles and JavaScript.

Development of a nanocomposite ultrafiltration membrane based on polyphenylsulfone blended with graphene oxide


In the present study, graphene oxide (GO) was incorporated as a nanoadditive into a polyphenylsulfone (PPSU) to develop a PPSU/GO nanocomposite membrane with enhanced antifouling properties. A series of membranes containing different concentrations (0.2, 0.5 and 1.0 wt.%) of GO were fabricated via the phase inversion method, using N-methyl pyrrolidone (NMP) as the solvent, deionized water as the non-solvent, and polyvinylpyrrolidone (PVP) as a pore forming agent. The prepared nanocomposite membranes were characterized using scanning electron microscopy (SEM) and atomic force microscopy (AFM), and were also characterized with respect to contact angle, zeta potential and porosity, mean pore radius, tortuosity and molecular weight cut-off (MWCO). Thermogravimetric analysis (TGA) and tensile testing were used to measure thermal and mechanical properties. The membrane performance was evaluated by volumetric flux and rejection of proteins, and antifouling properties. According to the results, the optimum addition of 0.5 wt% GO resulted in a membrane with an increased flux of 171 ± 3 Lm−2h−1 with a MWCO of ~40 kDa. In addition, the GO incorporation efficiently inhibited the interaction between proteins and the membrane surface, thereby improving the fouling resistance ability by approximately 58 ± 3%. Also, the resulting membranes showed a significant improvement in mechanical and thermal properties.


Membrane technology has shown great promise in all types of separation such as microfiltration (MF), ultrafiltration (UF), nanofiltration (NF) and reverse osmosis (RO). This technology has a number of attractive features such as simplicity of operating conditions, low energy consumption, no phase change, compact design and environmental friendliness1,2. Despite its great promise, membrane technology has a key limitation of membrane fouling. This is due to membrane surface properties including hydrophobicity, surface charge and roughness3,4,5,6. Fouling results in an increase in the operational cost, as well as decreased membrane life. Therefore, a large part of research in membrane technology is focused on the development of so-called antifouling membranes. To date, a number of techniques to develop antifouling membranes have been employed. They include hydrophilic surface modification by coating, grafting and the concept of making thin film composite (TFC) membranes, bulk modification by blending and mixing hydrophilic polymers, and incorporation of nanomaterials into membrane matrices for developing nanocomposite membranes1,7,8,9,10. Recently, the study of nanocomposite membranes has grown as an active area of membrane materials research and development. The nanomaterials of greatest interest for nanocomposite membrane development are titanium dioxide (TiO2), aluminium oxide (Al2O3), zinc oxide (ZnO), silicon dioxide (SiO2), carbon nanotubes (CNT) and graphene oxide (GO)11,12,13,14,15,16,17,18. Among them, GO is an emerging nanomaterial that has shown great promise in the development of anti-fouling nanocomposite membranes17,19,20,21,22,23. During the past few years, several investigators have studied the incorporation of GO into commonly used polymeric membrane matrices like polysulfone (PSF), polyethersulfone (PES), polyvinylidene difluoride (PVDF), polyacrylonitrile (PAN), and their copolymers, with the aim developing antifouling nanocomposite membranes19,24,25,26,27. The additional advantages of using GO as nanoadditive is that it can be processed easily owing to the availability of functional groups such as hydroxyl, carbonyl and carboxyl located on its surface and edge, which help to disperse it into the membrane matrix. Apart from these, its high hydrophilicity, antibacterial properties, low toxicity, chemical and biological durability and low cost make GO a very promising nanomaterial for the development of antifouling nanocomposite membranes17,24,28,29,30,31,32,33,34,35.

In the present study, GO was incorporated into a polyphenylsulfone, (PPSU) matrix to develop a flat-sheet nanocomposite membrane, hereafter called a PPSU/GO nanocomposite membrane. PPSU, a member of the family of sulfone polymers, is an outstanding material for preparing membranes with superior physical and chemical properties. Its great heat and chemical resistance, and long-term thermal and hydrolytic stability make PPSU a suitable membrane material for any water treatment applications. Despite their advanced features, PPSU membranes exhibit a hydrophobic nature that limits their long term-use in water process systems36,37. Hence, in this study, GO was mixed with PPSU to prepare a hydrophilic membrane, thereby reducing fouling, leading to enhanced cost-effectiveness by extending the operational lifetime and lowering energy requirements. To the best of our knowledge, GO has not yet been reported to improve the quality of a PPSU membrane, particularly to enhance the hydrophilicity of a PPSU membrane. More specifically, GO has not been investigated as a hydrophilic nanoadditive to prepare a PPSU/GO nanocomposite antifouling membrane. Hence, we prepared such a PPSU/GO nanocomposite membrane and reported the influence of GO addition with three different levels of GO content (0.2, 0.5, and 1.0 wt.%) on the properties of the nanocomposite membrane. The performance of the resultant nanocomposite membrane was evaluated in the terms of volumetric flux and the rejection of two model proteins of different molecular weights (bovine serum albumin BSA and pepsin), as well as its antifouling ability along with the adsorption of protein. The prepared PPSU/GO nanocomposite membrane exhibited superior separation performance compared to the pure PPSU membrane. The 0.5 wt.% GO-based nanocomposite membrane, which showed a flux of 171 ± 3 Lm−2h−1 and ~95% rejection of proteins, could be used as the preferred nanocomposite membrane in ultrafiltration applications.

Results and Discussion


Figure 1 shows both surface and cross-section morphologies of all the prepared membrane samples. As shown in the SEM images (Fig. 1a), the pure PPSU membrane had randomly distributed drop-like macro-voids. The walls of the macro-voids are thick and with closed ends. Also, a sponge layer was grown in a significant part of the membrane. Moreover, it was found that a thick skin layer was formed on top of a porous macro-void structure. With the addition of GO, the morphology of the nanocomposite membrane changed in many ways. Firstly, the pores in the sub porous layer of the membrane were relatively thinner and appeared in straight finger structures with open ends. Secondly, the thickness of the skin layer was reduced, and very fine oval-shaped pores were formed just under this thin-skin layer. Lastly, the spongy support layer thickness was also reduced but appeared much denser with interconnected pores compared with that of the PPSU membrane. Apart from these, it was found that the difference in the loading of GO in the PPSU matrix membrane afforded various types of structures. A membrane prepared from 0.2 wt.% GO exhibited small pores, residing underneath the skin layer (Fig. 1b), and the density and length of the pores increased for the membrane prepared from 0.5 wt.% GO (Fig. 1c). The pores stretched from the thin-skin layer to the supporting layer when the GO wt.% increased from 0.5 to 1.0% (Fig. 1d). Hence the membrane morphology, particularly of the porous sublayer, was found to depend on the loading of GO. Typically, this is due to a significant effect of hydrophilicity of the membrane casting solution with the GO concentration. The GO increases the exchange rate between the solvent and non-solvent during the precipitation process. This results in the development of a membrane with highly porous morphology coupled with dense pores and microscopic voids27,38. It can be seen in Fig. 2 that the surface roughness of the PPSU membrane is lower than the membrane prepared from GO, but among the membranes prepared with three different concentrations of GO (0.2, 0.5, 1.0 wt.%) the membrane with 0.5 wt.% GO showed higher values of roughness parameters. An addition of 0.5 wt.% GO resulted in significant changes in membrane topography features also. The large peaks and valleys were changed to a large number of small peaks and valleys, owing to the good compatibility of GO with the PPSU matrix. This led to a suitable surface structure being developed in the membrane.

Figure 1: SEM images of membrane top surface and cross-section morphologies.

(a) PPSU. (b) PPSU/GO 0.2 wt.%. (c) PPSU/GO 0.5 wt.%. (d) PPSU/GO 1.0 wt.%.

Figure 2: AFM 3D images of the prepared membranes surface.

(a) PPSU. (b) PPSU/GO 0.2 wt.%. (c) PPSU/GO 0.5 wt.%. (d) PPSU/GO 1.0 wt.%.

Thermal and mechanical properties

Figure 3(a) shows the thermal properties of the prepared membranes investigated at a temperature range of 100 °C to 650 °C. Results showed that the addition of GO to the PPSU matrix enhanced the thermal stability of the membrane. An increased thermal stability of the nanocomposite membranes is credited to the availability of the polar functional groups of GO, leading to the strong interfacial bonding between the PPSU matrix and the GO nanoadditive. The thermal properties of membranes with a GO content also have been described by other researchers29,39,40. Figure 3(b) shows the mechanical properties of the prepared membranes determined by the tensile test and defined by stress–strain curves with respect to three different GO contents. As shown in curve, the pure PPSU membrane showed a 3.5 ± 0.1 MPa tensile strength. This value increased to 3.8 ± 0.1 MPa when 1.0 wt.% GO was added. Furthermore, when the GO content increased from 0.2 wt.% to 0.5 no significant difference in tensile strength was observed. Meanwhile, at the higher level loading of GO, the elongation-at-break percentages decreased, reaching to 11.1 ± 0.1% for 0.2 wt.% GO, 10.5 ± 0.1% for 0.5 wt.%, and 9.9 ± 0.2% for 1.0 wt.% GO. The optimal mechanical properties for the membrane prepared from 1.0 wt.% GO can be credited to strong interaction between polymer matrix and GO owing to uniform dispersion of GO26,29,31. The above results were well in agreement with TGA and indicate that the PPSU/GO nanocomposite membranes also have good mechanical stability.

Figure 3

(a) Thermal properties and (b) mechanical properties using tensile tests of prepared membrane samples.

Hydrophilicity, porosity, mean pore radius and pore tortuosity

Figure 4(a) shows results of the contact angle analysis for the prepared membranes. As expected, the contact angle values were found to be dependent on the GO wt.%. According to the results, the pure PPSU membrane had a contact angle of 75 ± 2°. This value decreased to 52 ± 1° upon 0.2 wt.% loading of GO. The optimum contact angle of the nanocomposite membrane decreased to 41 ± 2°, when 0.5 wt.% GO was added. However, the contact angle value was found to increase to 45 ± 3° when 1.0 wt.% GO was added; this might be due to GO agglomeration in the PPSU matrix. The decreased contact angle for the nanocomposite membrane prepared with 0.5 wt.% GO was credited to the good dispersion of GO in the PPSU matrix, which generated more oxygenated contained functional groups on the membrane surface5,41. Similar observations were also reported for the GO in different polymeric matrices27,31,42. Subsequently, membrane porosity and volumetric flux were improved compared to the PPSU membrane, which is discussed in detail in the next section. The effect of GO concentrations on membrane overall porosity, mean pore radius and pore tortuosity can be observed in Fig. 4(b) and Table 1. In our investigation, we observed that when the GO content was 0.2 wt.% and 0.5 wt.%, the porosity initially increased in the range of 74 ± 1.4–80 ± 2.8%, decreasing its pore tortuosity. This can be explained on the basis of the low hydrophilic nature of GO in the PPSU matrix, which increased the solution thermodynamic instability in the phase inversion process and resulted in the formation of large pores on the membrane. When the GO concentration was increased to 1.0 wt.%, the porosity of the membrane was reduced to 75.5 ± 3.5%. This is credited to agglomeration of GO in the PPSU matrix upon higher loading, leading to a decrease in the exchange rate of the solvent and non-solvent (water) during the phase inversion process. Thus, the solvent was not properly leached out, which consequently led to a lower porosity as well as a reduced mean pore radius in the membrane. These phenomena were similar to those reported by other researchers27,43.

Figure 4: Membrane properties of PPSU, PPSU/GO 0.2 wt.%, PPSU/GO 0.5 wt.% and PPSU/GO 1.0 wt.% membranes.

(a) Water contact angle. (b) Overall porosity determined by the gravimetric method. (c) The surface zeta potential as a function of pH. (d) The surface pore size in terms of MWCO using a 1 g/L neutral solution of PEG and PEO.

Table 1 Mean pore radius (rm), and tortuosity (τ) of the nanocomposite ultrafiltration membranes.

Zeta potential and molecular weight cut-off

The zeta potential of the prepared membranes evaluated from streaming potential and streaming current measurements is shown in Fig. 4(c). The zeta potential, which determines the antifouling performance of the membrane, was significantly increased by increasing the GO content of the PPSU matrix. A membrane prepared with a higher concentration of GO had a more negative value than the pure PPSU membrane owing to the increase in the oxygen-containing functional groups on the membrane surface. According to the results, the zeta potential values at maximum pH ~8.5 were −10 mV for PPSU, −12 mV for nanocomposite PPSU/GO 0.2 wt.%, −14 mV for PPSU/GO 0.5 wt.% and −18 mV for PPSU/GO 1.0 wt.%, respectively. As observed in the results, the pure PPSU membrane showed a less negative zeta potential than the nanocomposite membrane. Therefore, BSA did not adhere to the membrane surface, leading to the membrane being less fouled. Hence, addition of GO to the PPSU matrix helped to construct a membrane with a negatively charged surface, which led to a significant increase in the electrostatic repulsion between the membrane and proteins and support of the antifouling performance. Figure 4(d) shows the results of MWCO. MWCO is a pore characteristic of the membranes and it is related to 90% rejection of given neutral solute. As revealed in the results, the addition of GO in PPSU solution increased MWCO of the PPSU/GO nanocomposite membrane progressively from ~25 kDa to ~40 kDa. An increasing MWCO of the membrane is due to an availability of functional groups of GO, leading to increase the solution thermodynamic instability in the phase inversion process, thereby significantly increased the pore. As is known that MWCO has a linear relationship with the pore size of the membrane.

Pure water volumetric flux and protein rejection

Figure 5(a) shows the influence of GO content on membrane flux at a pressure of 2 bar. As can be clearly seen in the results, the volumetric flux of the pure PPSU membrane was 119 ± 3 Lm−2h−1. It reached 164 ± 2 Lm−2h−1 and 171 ± 3 Lm−2h−1 when 0.2 and 0.5 wt.% GO were incorporated. However, for 1.0 wt.% of GO the volumetric flux of the membrane was found to decrease, reaching 165 ± 1 Lm−2h−1. After a certain time period, the flux of the PPSU membrane declined up to 20 ± 1%, while the fluxes for the PPSU/GO nanocomposite membranes were almost constant, demonstrating that membranes prepared with GO have antifouling properties owing to the enhancement of their hydrophilicity and lower values of tortuosity of the membrane44. However, as the concentration of GO increased to 1.0 wt.% the decrease in the flux became more pronounced. The decrease in the flux can be explained by the increase in the entire membrane resistance, which mainly resulted from reduced surface porosity due to fouling, a greater thickness of the skin layer and suppression of the finger-like pores. Table 2 illustrates rejection of the model proteins BSA (69 kDa) and pepsin (35 kDa) by all the prepared membranes. During experiment, it was observed that protein rejection through PPSU membrane remained constant for the first 40 minutes, then rejection level increased over increasing time, meanwhile membrane flux decreased. This can be explained by the effect of fouling as well as concentration polarization caused by the electrostatic interaction between the solutions and the membrane surface charge. The rejection of both proteins BSA and pepsin were significantly enhanced with the addition of GO contents, as expected. Generally, the protein rejection is dominated by the sieving behaviour, which is determined by the membrane pore size and molecular weight of the solute, as well as the electrostatic interaction owing to membrane surface charge properties and solute isoelectric points under different pH conditions45. As to the size of the proteins, BSA has a larger size than pepsin, hence BSA was repelled significantly by the nanocomposite membrane42,46. As to the surface charge of the proteins at pH 7 ± 0.2, BSA (pI–4.8) shows a lower net negative charge and pepsin (pI- 1) indicates a higher net negative charge. According to Fig. 4(c), the surface zeta potential values of the membranes varied with the GO contents and reached values of −12 mV, −13 mV and −18 mV, respectively, at pH 7 ± 0.2. These values indicate a strong electrostatic repulsion between the protein molecules and the surface of the membrane; thus, the nanocomposite membrane showed a significant rejection of BSA and pepsin. In a continuation of the study of membrane fouling, protein adsorption and flux recovery ratio are discussed in the next sections.

Figure 5: Membrane performance of PPSU, PPSU/GO 0.2 wt.%, PPSU/GO 0.5 wt.% and PPSU/GO 1.0 wt.% membranes.

(a) Time-dependent pure water volumetric fluxes of the prepared membranes at 2 bar TMP. (b) Time-dependent fluxes of pure water, PB, and BSA protein and after fouled membranes.

Table 2 A performance of PPSU and PPSU/GO nanocomposite ultrafiltration membranes.

Antifouling property

The antifouling property of the pure PPSU and PPSU/GO nanocomposite membranes were analysed by the flux recovery, total fouling, reversible volumetric flux decline and irreversible volumetric flux decline of pure water and phosphate buffer solution after fouling by 1 g/L BSA solution as shown in Fig. 5(b). It can be observed in the results that the permeation rate of the membranes in all of the steps followed a similar trend, i.e., the volumetric flux of water as well as the phosphate buffer solution was much greater than the flux of the BSA solution. The BSA volumetric flux declined dramatically as a function of time for the pure PPSU membrane. The rate of flux decline indicated the higher fouling tendency caused by the deposition and adsorption of protein molecules on the membrane pores and surface. The PPSU/GO nanocomposite membranes retained their volumetric fluxes well at the end of protein filtration and showed the highest fluxes compared with the pure PPSU membrane. This can be explained by the effect of the GO contents, which improved membrane properties including hydrophilicity, surface charge and morphology30,31,32,47. Therefore, the nanocomposite membrane surface attracted fewer protein molecules than the pure PPSU membrane. The JvRR, FtR, JvrD and JvirD were calculated and the values are depicted in Table 2. After washing with phosphate buffer solution for the first cycle of volumetric flux, the JvRR values were 46 ± 2.1%, 78 ± 1.5%, 89 ± 4.9% and 87 ± 1.1% for the PPSU, PPSU/GO 0.2 wt.%, PPSU/GO 0.5 wt.% and PPSU/GO 1.0 wt.% membranes, respectively. The second cycle of JvRR (%) analysed by pure water volumetric flux were 55 ± 2.9%, 82 ± 1.9%,95 ± 1.4% and 91 ± 4.2% for the PPSU membrane with a GO content of 0.2 wt.%, 0.5 wt.% and 1.0 wt.%, respectively. These values indicated that the higher the flux recovery ratio, the better the antifouling properties of the membranes. The greatest antifouling performance was obtained by 0.5 wt.% of GO blended with the PPSU polymer matrix membrane. The high JvRR, in the case of the nanocomposite membrane, can be credited to the combined effects of high negative zeta potential (Fig. 4c), lower roughness and high hydrophilicity (Fig. 4a) of the membrane surface, which prevented fouling as well as the adsorption of protein molecules on the surface48. The introduction of GO also resulted in the changes of membrane pore sizes and thereby significantly affect membrane fouling rate. The obtained JvRR, FtR, JvrD and JvirD trend were also explained by the results of AFM images presented in Fig. 2. As shown in these images, the pure PPSU membrane had a surface with a larger area of ridge-valley structure, while the nanocomposite membrane showed a relatively smooth surface and there was found to be less of a ridge-valley structure; thus, proteins could not accumulate in the “valleys”. Therefore, the fouling possibility decreased, leading to a higher JvRR. These results demonstrated a significant role of GO in developing antifouling nanocomposite membranes and the prepared membrane can be used extensively in ultrafiltration processes.

Protein adsorption

To evaluate the antifouling property of a membrane, a protein adsorption experiment was carried out by keeping the membrane in protein solutions for a certain time period. The adsorption results are provided in Table 2. According to the results, the adsorption percentage decreased significantly from 59.2 ± 2.5 μg/cm2 to 21.1 ± 2.6 μg/cm2 for PPSU and PPSU/GO nanocomposite membranes owing to the higher hydrophilic nature of the membrane confirmed by the water contact angle and zeta potential. Lowering protein adsorption in the case of nanocomposite membranes has been explained very briefly in earlier sections. Finally, the results revealed that PPSU/GO nanocomposite membranes had a better ability to repel the larger protein molecules (as shown in Fig. 6) and more reliable antifouling properties than the PPSU membrane and can be used in the food processing industry, pharmaceutical industry, waste water treatment, and separation of macromolecules such as bacteria, viruses, enzymes and proteins.

Figure 6

Schematic illustration of nanocomposite membrane surface and protein molecules interactions.


Graphene oxide (GO) at three different concentrations (0.2, 0.5 and 1.0 wt.%) was incorporated into a polyphenylsulfone (PPSU) matrix to develop PPSU/GO nanocomposite membranes. The separation performance of the prepared membranes was evaluated by measurements of volumetric flux and rejection of BSA and pepsin as well as their antifouling properties, all as a function of the GO concentration. The results showed that the figure of merit for separation by the membrane prepared with GO showed a significant dependence on the GO concentration. The addition of GO with 0.5 wt.% resulted in a nanocomposite membrane with increased surface hydrophilicity that increased the volumetric flux from 119 ± 4 Lm−2h−1 to 171 ± 3 Lm−2h−1 with a MWCO of ~25 to ~40 kDa. The fouling resistance of the membrane was significantly improved with an optimal addition of GO (0.5 wt.%) as a result of the increase in the hydrophilicity, roughness and negative zeta potential values of the membrane surface that mitigates the protein adsorption on the membrane surface. An incorporation of GO efficiently inhibited the interaction between protein and membrane surface and thereby improved the fouling resistance by 58 ± 3%. Moreover, the membranes with GO addition showed a significant improvement in mechanical and thermal properties.

Materials and Methods


Polyphenylsulfone (PPSU) (Radel® -R5500) was purchased from Solvay Advanced Polymer (Belgium). N-methyl-pyrrolidone (NMP) and polyvinylpyrrolidone (PVP, 10 k) were used without any further purification from Oxford Lab Chem (India). Graphene oxide (GO), bovine serum albumin (BSA), pepsin, potassium dihydrogen phosphate, disodium hydrogen phosphate dehydrate, polyethylene oxide (PEO, MW of 10 kDa), and polyethylene glycol (PEG, MW 35 kDa) were purchased from Sigma Aldrich (USA) and potassium chloride was purchased from Acros Organics (USA). Hydrochloric acid was purchased from Fisher Chemical (UK), sodium lauryl sulfate GRG from Winlab (UK) and polyethylene glycol (PEG, average MWs of 600 Da, 1 kDa, 4 kDa, 10 kDa and 30 kDa, potassium dichromate and sodium azide from Merck (Germany). Deionized water (Milli-Q) with a resistivity of 18.2 MΩ cm was used throughout the experiments (Millipore, USA).

Preparation of PPSU/GO nanocomposites

To prepare the PPSU/GO nanocomposite membrane matrix, the PPSU and GO were first dried for 12 h at 50 °C to remove moisture content. Then, a certain amount of GO (0.2, 0.5 and 1.0 wt.%) was added to the NMP and sonicated using an digital sonifier (Branson Ultrasonics Corporation, USA) for 1 h to disperse the GO. Then the uniformly dispersed GO was mixed with the solution prepared by dissolving 17.5 wt.% PPSU and 1.0 wt.% PVP into 81.5 wt.% NMP. After stirring at 50 rpm and 70 °C for 24 h, the resulting homogeneous solution was kept until no air bubbles appeared in the solution. This was the membrane casting solution.

Fabrication of membranes

The prepared solution of the PPSU/GO nanocomposites was cast on a clean glass plate using a casting knife film applicator (DeltaE Srl, Italy). Then, the cast film with a thickness of 150 μm was immediately immersed in a non-solvent bath of distilled water mixed with 0.5 g/L of sodium lauryl sulfate at 15 ± 2 °C to complete the phase separation. The fabricated (so-called PPSU, PPSU/GO 0.2 wt.%, PPSU/GO 0.5 wt.% and PPSU/GO 1.0 wt.%) nanocomposite membranes were preserved in deionized water containing 0.2% sodium azide to avoid microbial contamination until use.

Membrane morphology

The cross-section morphology of the prepared membranes was examined by scanning electron microscopy (SEM; JEOL, Japan). For examination, the membrane sample was cut into pieces of various sizes and immersed in liquid nitrogen. The frozen membrane was broken and pasted onto an SEM stub with the help of conductive double-sided carbon tape. Then, the stub with the pasted samples was gold sputtered. The membrane surface topographies were analysed by atomic force microscopy (AFM) using a Nanosurf® Mobile S scanning probe-optical microscope (Switzerland). For this analysis, the sample was cut into small pieces with a size of 2 mm × 2 mm and pasted onto the sample holder using adhesive tape. Then the sample holder was placed on the AFM scanner and an optical head.

Thermal and mechanical stability measurement

The thermal stability of the membrane samples was investigated by thermogravimetric analysis (TGA; Mettler Toledo, Austria). For this test, a 10 mg sample was placed in a ceramic crucible and analysed under an inert nitrogen atmosphere (100 mL/min) under dynamic conditions between 100 °C and 650 °C at a heating rate of 10 °C/min. The mechanical properties of the membrane samples were studied using the LR5K Plus tensile test machine (Lloyd Instruments Ltd., United Kingdom). For each sample, the values of the tensile strength, breaking stress and breaking elongation were determined as the average of at least triplicate membrane samples.

Contact angle, porosity, mean pore radius and pore tortuosity measurement

The membrane surface wettability was analysed by the contact-angle measuring instrument Attension T330 (Biolin Scientific). The measurements of all samples for the contact angle between the water and the membrane surfaces were performed using deionized water as the analysis liquid. Deionized water (3 μL) was dropped in six random locations on the dried membrane surface and the average value was reported.

The porosity (ε) of the membrane was determined by the gravimetric method, as defined in the following eq. (1) 27:

where, WW: weight of the wet membrane, WD: weight of the dry membrane, A: membrane effective area (m2), ρ: water density (0.998 gcm−3) and lm: membrane thickness (m).

The mean pore radius of the membranes was determined by using porosity and water flux values, and was calculated by the Guerout–Elford–Ferry eq. (2) 26,27,48:

where, rm: mean pore radius (nm), η: water viscosity (8.9 × 10−4 Pa s), Q: volume of the permeated pure water per unit time (m3s−1) and ΔP: operation pressure (2 bar).

The tortuosity (τ) of membrane was determined by using eq. (3) 44,49:

Zeta potential measurement

The surface charge of the membrane was evaluated by zeta potential measurement using the SurPASS electro-kinetic analyser (Anton-Paar KG, Graz, Austria) based on a streaming potential and streaming current measurement. Experiments were carried out in an adjustable clamping cell and pH titration was performed from pH 2 to 9 using a solution of 0.01 mM KCl and 0.25 M HCl (acid). The resultant values of zeta potential were determined on two membrane samples for each type of membrane.

MWCO measurement

The surface pore size of the membrane was measured in terms of MWCO using a 1 g/L neutral solution of polyethylene glycol and polyethylene oxide with different molecular weights from 600 Da to 100 kDa. The solutions were prepared individually using deionized (Milli-Q) water. Experiments were carried out on the cross-flow membrane set-up at 1 bar transmembrane pressure (TMP) at room temperature. In addition, solute concentrations of organic carbon in the feed and permeate samples were analysed by a Sievers 5310 C total organic carbon (TOC) analyser (GE Analytical Instruments). The solute rejection (R) percentage was calculated by the following eq. (4):

where, Cp: concentration of PEG in the permeate and Cf: concentration of PEG in the feed.

Volumetric flux and protein rejection

The ultrafiltration performance of the membranes was carried out using a pressure-driven filtration CF042 cross-flow membrane module, Sterlitech Corporation (USA), where the effective membrane area was 42 cm2. The water permeation performance was determined by allowing deionized water (Milli-Q) to pass through the membranes using the above-mentioned cross-flow filtration system. Initially, membranes were compacted at 3 bar of TMP for 2 h to remove any remaining solvent or unreacted polymer. After compaction, values of volumetric flux at constant TMP (2 bar) were measured every 1 h for 14 h under steady-state conditions at room temperature. The flux was calculated using the following eq. (5):

where, Jv: volumetric flux (Lm−2h−1), V: volumetric flow rate of permeating water (Lh−1), A: effective surface area of the membrane (m2) and ΔT: sampling time (h).

The protein rejection experiment was performed using 1 g/L BSA or pepsin as feed solutions prepared in a phosphate buffer (0.1 M, pH 7 ± 0.2). The rejection experiments were performed at a 2 bar transmembrane pressures (TMP) for 1 h and room temperature. The protein concentrations in the feed and permeate were determined by a UV spectrophotometer (Agilent Technologies, Cary 60 UV–Vis) at a wavelength of 280 nm. The rejection value was calculated using eq. (4).

Antifouling studies

For the antifouling studies, three cycles of experiments were carried out for each membrane sample. The antifouling property and volumetric flux recovery ratio (JvRR) of the membrane were measured using the following steps: First of all, a pure water volumetric flux was performed at 2 bar TMP for 180 min, then, initial volumetric flux of the membrane measured using 0.1 mol/L phosphate buffer (PB) under the above-mentioned condition. After this, a 1 g/L of aqueous solution of BSA as a fouling agent (pH 7.0 maintained by PB) was filtered for 240 min and the volumetric flux profile with time was recorded. After filtration of the BSA solutions, the fouled membranes were washed again using PB and the final phosphate-buffered volumetric flux was measured. Thereafter, the water volumetric flux was measured again up to 180 min for the membrane and total procedure time of 960 min.

Finally, for measuring the antifouling property of the membrane samples, the volumetric flux recovery ratio (JvRR), total fouling ratio (FtR), reversible volumetric flux decline ratio (JvrD), and irreversible volumetric flux decline ratio (JvirD) were calculated using the following eqs (6, 7, 8, 9) 27:

where, Jvi: initial water or PB, Jvf: final water or PB, and Jvp: protein volumetric flux.

Protein adsorption studies

Further, the antifouling property of the prepared membrane was measured by a protein adsorption test. For this measurement, BSA was used as a model protein to evaluate the anti-protein-adsorption performance. For the experiment, the membrane samples were cut into pieces with a 9 cm2 surface area and treated by ultra-sonication for 20 min in a phosphate-buffered solution (pH 7.0 ± 0.2) for cleaning. Then, the pre-treated membranes were kept in a phosphate-buffered BSA solution (1.0 g/L) for 24 h to attain adsorption–elution equilibrium at room temperature. After the adsorption of protein, each membrane was taken out of the solution. The initial and final concentrations of protein in the solution were determined on the basis of the absorbance wavelength. The protein concentration was measured using the Bradford micro-assay technique27 against a standard of pure protein solution. The apparent amounts of BSA adsorbed by the membranes were calculated using the eq. (10) 50:

where, Ci: initial concentration of protein solution, and Cf: final concentration of protein solution.

Additional Information

How to cite this article: Shukla, A. K. et al. Development of a nanocomposite ultrafiltration membrane based on polyphenylsulfone blended with graphene oxide. Sci. Rep. 7, 41976; doi: 10.1038/srep41976 (2017).

Publisher's note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.


  1. 1

    Shannon, M. et al. Science and technology for water purification in the coming decades. Nature 452, 301–310 (2008).

    ADS  CAS  Google Scholar 

  2. 2

    Liu, Y., Zhang, S. & Wang, G. The preparation of antifouling ultrafiltration membrane by surface grafting zwitterionic polymer onto poly(arylene ether sulfone) containing hydroxyl groups membrane. Desalination 316, 127–136 (2013).

    CAS  Google Scholar 

  3. 3

    Huang, J. et al. A novel composite conductive microfiltration membrane and its anti-fouling performance with an external electric field in membrane bioreactors. Sci. Rep. 5, 9268 (2015).

    CAS  PubMed  PubMed Central  Google Scholar 

  4. 4

    Yu, W., Xu, L., Graham, N. & Qu, J. Pre-treatment for ultrafiltration: effect of pre-chlorination on membrane fouling. Sci. Rep. 4, 6513 (2014).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  5. 5

    Vatanpour, V., Shockravi, A., Zarrabi, H., Nikjavan, Z. & Javadi, A. Fabrication and characterization of anti-fouling and anti-bacterial Ag-loaded graphene oxide/polyethersulfone mixed matrix membrane. J. Ind. Eng. Chem. 30, 342–352 (2015).

    CAS  Google Scholar 

  6. 6

    Nasreen, S. A. A. N., Sundarrajan, S., Syed Nizar, S. A., Balamurugan, R. & Ramakrishna, S. In situ polymerization of PVDF-HEMA polymers: electrospun membranes with improved flux and antifouling properties for water filtration. Polym. J. 46, 167–174 (2013).

    Google Scholar 

  7. 7

    Parashuram, K. et al. Tailoring the molecular weight cut off values of polyacrylonitrile based hollow fibre ultrafiltration membranes with improved fouling resistance by chemical modification. J. Memb. Sci. 425–426, 251–261 (2013).

    Google Scholar 

  8. 8

    Lohokare, H. R., Muthu, M. R., Agarwal, G. P. & Kharul, U. K. Effective arsenic removal using polyacrylonitrile-based ultrafiltration (UF) membrane. J. Memb. Sci. 320, 159–166 (2008).

    CAS  Google Scholar 

  9. 9

    Huang, L. et al. In situ immobilization of silver nanoparticles for improving permeability, antifouling and anti-bacterial properties of ultrafiltration membrane. J. Memb. Sci. 499, 269–281 (2016).

    ADS  CAS  Google Scholar 

  10. 10

    Semblante, G. U., You, S. J., Wu, G. H., Chang, T. C. & Yen, F. C. Pore size and flux behavior of polyvinylidene fluoride and polymethyl vinyl ether-alt-maleic anhydride with TiO2 . Chem. Eng. J. 241, 513–520 (2014).

    CAS  Google Scholar 

  11. 11

    Yu, W., Xu, L., Graham, N. & Qu, J. Contribution of Fe3O4 nanoparticles to the fouling of ultrafiltration with coagulation pre-treatment. Sci. Rep. 5, 13067 (2015).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  12. 12

    Garcia-ivars, J., Iborra-clar, M. & Alcaina-miranda, M. Development of fouling-resistant polyethersulfone ultrafiltration membranes via surface UV photografting with polyethylene glycol/aluminum oxide nanoparticles. Sep. Purif. Technol. 135, 88–99 (2014).

    CAS  Google Scholar 

  13. 13

    Rabiee, H., Vatanpour, V., Farahani, M. H. D. A. & Zarrabi, H. Improvement in flux and antifouling properties of PVC ultrafiltration membranes by incorporation of zinc oxide (ZnO) nanoparticles. Sep. Purif. Technol. 156, 299–310 (2015).

    CAS  Google Scholar 

  14. 14

    Jin, L. et al. Preparation and characterization of a novel PA-SiO2 nanofiltration membrane for raw water treatment. Desalination 298, 34–41 (2012).

    CAS  Google Scholar 

  15. 15

    Hamid, N. A. A. et al. Morphological and separation performance study of polysulfone/titanium dioxide (PSF/TiO2) ultrafiltration membranes for humic acid removal. Desalination 273, 85–92 (2011).

    CAS  Google Scholar 

  16. 16

    Das, R., Ali, M. E., Hamid, S. B. A., Ramakrishna, S. & Chowdhury, Z. Z. Carbon nanotube membranes for water purification: A bright future in water desalination. Desalination 336, 97–109 (2014).

    CAS  Google Scholar 

  17. 17

    Zinadini, S. et al. Preparation and characterization of antifouling graphene oxide/polyethersulfone ultrafiltration membrane: Application in MBR for dairy wastewater treatment. J. Water Process Eng. 7, 280–294 (2015).

    Google Scholar 

  18. 18

    Inukai, S. et al. High-performance multi-functional reverse osmosis membranes obtained by carbon nanotube·polyamide nanocomposite. Sci. Rep. 5, 13562 (2015).

    ADS  PubMed  PubMed Central  Google Scholar 

  19. 19

    Safarpour, M., Vatanpour, V. & Khataee, A. Preparation and characterization of graphene oxide/TiO2 blended PES nanofiltration membrane with improved antifouling and separation performance. Desalination 393, 65–78 (2016).

    CAS  Google Scholar 

  20. 20

    Yin, J., Zhu, G. & Deng, B. Graphene oxide (GO) enhanced polyamide (PA) thin-film nanocomposite (TFN) membrane for water purification. Des 379, 93–101 (2015).

    Google Scholar 

  21. 21

    Choi, W., Lahiri, I., Seelaboyina, R. & Kang, Y. S. Synthesis of Graphene and Its Applications: A Review. Crit. Rev. Solid State Mater. Sci. 35, 52–71 (2010).

    ADS  CAS  Google Scholar 

  22. 22

    Suk, J. W., Piner, R. D., An, J. & Ruoff, R. S. Mechanical properties of monolayer graphene oxide. ACS Nano 4, 6557–64 (2010).

    CAS  PubMed  Google Scholar 

  23. 23

    Surwade, S. P. et al. Water desalination using nanoporous single-layer graphene. Nat. Nanotechnol. 10, 459–64 (2015).

    ADS  CAS  PubMed  Google Scholar 

  24. 24

    Zhao, C., Xu, X., Chen, J., Wang, G. & Yang, F. Highly effective antifouling performance of PVDF/graphene oxide composite membrane in membrane bioreactor (MBR) system. Desalination 340, 59–66 (2014).

    CAS  Google Scholar 

  25. 25

    Chong, J. Y., Aba, N. F. D., Wang, B., Mattevi, C. & Li, K. UV-Enhanced Sacrificial Layer Stabilised Graphene Oxide Hollow Fibre Membranes for Nanofiltration. Sci. Rep. 5, 15799 (2015).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  26. 26

    Yu, L. et al. Preparation and characterization of HPEI-GO/PES ultrafiltration membrane with antifouling and antibacterial properties. J. Memb. Sci. 447, 452–462 (2013).

    CAS  Google Scholar 

  27. 27

    Zinadini, S., Zinatizadeh, A. A., Rahimi, M., Vatanpour, V. & Zangeneh, H. Preparation of a novel antifouling mixed matrix PES membrane by embedding graphene oxide nanoplates. J. Memb. Sci. 453, 292–301 (2014).

    CAS  Google Scholar 

  28. 28

    Filice, S. et al. Graphene oxide and titania hybrid Nafion membranes for efficient removal of methyl orange dye from water. Carbon N. Y. 82, 489–499 (2015).

    CAS  Google Scholar 

  29. 29

    He, Y., Tong, C., Geng, L., Liu, L. & Lü, C. Enhanced performance of the sulfonated polyimide proton exchange membranes by graphene oxide: Size effect of graphene oxide. J. Memb. Sci. 458, 36–46 (2014).

    CAS  Google Scholar 

  30. 30

    Liu, C. X., Zhang, D. R., He, Y., Zhao, X. S. & Bai, R. Modification of membrane surface for anti-biofouling performance: Effect of anti-adhesion and anti-bacteria approaches. J. Memb. Sci. 346, 121–130 (2010).

    CAS  Google Scholar 

  31. 31

    Lee, J. et al. Graphene oxide nanoplatelets composite membrane with hydrophilic and antifouling properties for wastewater treatment. J. Memb. Sci. 448, 223–230 (2013).

    CAS  Google Scholar 

  32. 32

    Qin, D., Liu, Z., Delai Sun, D., Song, X. & Bai, H. A new nanocomposite forward osmosis membrane custom-designed for treating shale gas wastewater. Sci. Rep. 5, 14530 (2015).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  33. 33

    Hu, M. & Mi, B. Layer-by-layer assembly of graphene oxide membranes via electrostatic interaction. J. Memb. Sci. 469, 80–87 (2014).

    ADS  CAS  Google Scholar 

  34. 34

    Sun, X.-F. et al. Graphene oxide–silver nanoparticle membrane for biofouling control and water purification. Chem. Eng. J. 281, 53–59 (2015).

    CAS  Google Scholar 

  35. 35

    Kang, S.-H., Fang, T.-H. & Hong, Z.-H. Electrical and mechanical properties of graphene oxide on flexible substrate. J. Phys. Chem. Solids 74, 1783–1793 (2013).

    ADS  Google Scholar 

  36. 36

    Wang, T., Wang, Y.-Q., Su, Y.-L. & Jiang, Z.-Y. Antifouling ultrafiltration membrane composed of polyethersulfone and sulfobetaine copolymer. J. Memb. Sci. 280, 343–350 (2006).

    CAS  Google Scholar 

  37. 37

    Liu, Y. et al. Synthesis of sulfonated polyphenylsulfone as candidates for antifouling ultrafiltration membrane. Sep. Purif. Technol. 98, 298–307 (2012).

    ADS  CAS  Google Scholar 

  38. 38

    Manickam, S. S., Gelb, J. & McCutcheon, J. R. Pore structure characterization of asymmetric membranes: Non-destructive characterization of porosity and tortuosity. J. Memb. Sci. 454, 549–554 (2014).

    CAS  Google Scholar 

  39. 39

    Ding, R. et al. Graphene oxide-embedded nanocomposite membrane for solvent resistant nanofiltration with enhanced rejection ability. Chem. Eng. Sci. 138, 227–238 (2015).

    CAS  Google Scholar 

  40. 40

    Shao, D. et al. PANI/GO as a super adsorbent for the selective adsorption of uranium(VI). Chem. Eng. J. 255, 604–612 (2014).

    CAS  Google Scholar 

  41. 41

    Zhang, J. et al. Synergetic effects of oxidized carbon nanotubes and graphene oxide on fouling control and anti-fouling mechanism of polyvinylidene fluoride ultrafiltration membranes. J. Memb. Sci. 448, 81–92 (2013).

    ADS  CAS  Google Scholar 

  42. 42

    Xu, Z. et al. Organosilane-functionalized graphene oxide for enhanced antifouling and mechanical properties of polyvinylidene fluoride ultrafiltration membranes. J. Memb. Sci. 458, 1–13 (2014).

    CAS  Google Scholar 

  43. 43

    Xia, S. & Ni, M. Preparation of poly(vinylidene fluoride) membranes with graphene oxide addition for natural organic matter removal. J. Memb. Sci. 473, 54–62 (2015).

    CAS  Google Scholar 

  44. 44

    Srisurichan, S., Jiraratananon, R. & Fane, A. G. Mass transfer mechanisms and transport resistances in direct contact membrane distillation process. J. Memb. Sci. 277, 186–194 (2006).

    CAS  Google Scholar 

  45. 45

    Li, Q., Bi, Q. yan, Lin, H. H., Bian, L. X. & Wang, X. L. A novel ultrafiltration (UF) membrane with controllable selectivity for protein separation. J. Memb. Sci. 427, 155–167 (2013).

    ADS  CAS  Google Scholar 

  46. 46

    Kanagaraj, P., Nagendran, A., Rana, D., Matsuura, T. & Neelakandan, S. Separation of macromolecular proteins and rejection of toxic heavy metal ions by PEI/cSMM blend UF membranes. Int. J. Biol. Macromol. 72, 223–9 (2015).

    CAS  PubMed  Google Scholar 

  47. 47

    Safarpour, M., Vatanpour, V., Khataee, A. & Esmaeili, M. Development of a novel high flux and fouling-resistant thin film composite nanofiltration membrane by embedding reduced graphene. Sep. Purif. Technol. 154, 96–107 (2015).

    CAS  Google Scholar 

  48. 48

    Safarpour, M., Khataee, A. & Vatanpour, V. Effect of reduced graphene oxide/TiO2 nanocomposite with different molar ratios on the performance of PVDF ultrafiltration membranes. Sep. Purif. Technol. 140, 32–42 (2015).

    CAS  Google Scholar 

  49. 49

    Abu-Zeid, M. A. E.-R. et al. A comprehensive review of vacuum membrane distillation technique. Desalination 356, 1–14 (2015).

    CAS  Google Scholar 

  50. 50

    Zhang, X. et al. Preparation, performance and adsorption activity of TiO2 nanoparticles entrapped PVDF hybrid membranes. Appl. Surf. Sci. 263, 660–665 (2012).

    ADS  CAS  Google Scholar 

Download references


The authors are thankful for the financial support of the King Abdullah Institute for Nanotechnology, Deanship of Scientific Research, King Saud University, Riyadh, Saudi Arabia.

Author information




A.K.S., J.A. and M.A. contemplated the scientific idea and designed the experiments. A.K.S. and J.A. developed the methodology, prepared the membranes and performed the experiments. J.A. and L.A.D. performed the AFM, TGA and tensile testing. M.M.R. carried out the zeta potential and MWCO analysis. J.A. contributed with SEM. A.K.S. characterised the membranes with regard to contact angle, porosity, mean pore radius and tortuosity. M.A. supervised the research team. A.K.S. and J.A. analysed and interpreted all the data and wrote the manuscript. All authors contributed to and proofread the manuscript.

Corresponding author

Correspondence to Javed Alam.

Ethics declarations

Competing interests

The authors declare no competing financial interests.

Rights and permissions

This work is licensed under a Creative Commons Attribution 4.0 International License. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in the credit line; if the material is not included under the Creative Commons license, users will need to obtain permission from the license holder to reproduce the material. To view a copy of this license, visit

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Shukla, A., Alam, J., Alhoshan, M. et al. Development of a nanocomposite ultrafiltration membrane based on polyphenylsulfone blended with graphene oxide. Sci Rep 7, 41976 (2017).

Download citation

Further reading


By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.


Quick links

Nature Briefing

Sign up for the Nature Briefing newsletter — what matters in science, free to your inbox daily.

Get the most important science stories of the day, free in your inbox. Sign up for Nature Briefing