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Fast preparation of a polydopamine/ceramic composite nanofiltration membrane with excellent permselectivity

Chaoyue Wanga, Hanyang Wub, Gaosheng Yua, Haoran Zhab and Runlin Han*a
aSchool of Chemistry and Chemical Engineering, Jinggangshan University, Ji'an 343009, China. E-mail: hanrunlin@163.com; Tel: +86-13842712519
bJiangxi Bocent Environmental Technology Co., Ltd, Pingxiang 337200, China

Received 3rd November 2022 , Accepted 15th December 2022

First published on 23rd December 2022


Abstract

Fabrication of a dense polymer/ceramic composite membrane with high permeability remains a great challenge. In this study, a highly selective polydopamine (PDA)/ceramic composite nanofiltration (NF) membrane was prepared by using an Al2O3 ceramic membrane with pore size of 0.1 μm as the support layer. In order to improve the membrane formation rate, KMnO4 was introduced to oxidize the dopamine to improve the reactivity, and Na2CO3 was used to adjust the pH value of the dopamine solution. When the addition amount of KMnO4 is 0.2 g L−1 and that of Na2CO3 is 1 g L−1, a functional layer can be formed within 10 min. PDA and polyethyleneimine (PEI) were added to the functional layer to adjust the selectivity of the composite membrane. The composite membrane showed a rejection of 99.7% towards Congo red dye with a high flux of 165 L (m2 h bar)−1 at ambient temperature. After 3 h treatment with Congo red, the fouling resistance of the membrane was improved compared with that of the ceramic based membrane. The surface morphology and composition of the composite membrane were also characterized with scanning electron microscopy (SEM) and X-ray photoelectron spectroscopy (XPS), which confirmed the successful preparation of the PDA/ceramic composite membrane.


1 Introduction

With rapid urbanization, water environment problems are becoming more and more serious. There are many ways to treat waste water, including adsorption, chemical oxidation, precipitation and filtration.1–3 However, waste water treatment with low energy consumption is still urgently needed. Membrane separation technology has the advantages of low energy consumption, small footprint and easy integration, and is widely used in the petrochemical industry, biological medicine industry, waste water treatment and other fields. Nanofiltration (NF) with high flux and selectivity is widely used in the precise separation of small molecules during 200–1000 Da and ions with high valence. It is generally believed that the separation mechanism of NF membrane is the synergistic effect of size-sieving and Donnan repulsion.4 Most commercial NF membranes are polymeric, because the pore size and surface property of polymer membrane are easy to adjust, while ceramic NF membranes are difficult to obtain because preparation of dense functional layers without defect needs special technology.5 The common functional layer materials of commercial composite NF membrane are polyamide and sulfonated polysulfone, while the supporting layer material is polysulfone, polyvinylidene fluoride or polyimide.6 However, these kinds of polymer membrane often have some problems, such as low solvent resistance, acid and alkali resistance, oxidation resistance or thermal resistance. In contrast, inorganic membranes such as Al2O3 membrane, zeolite membrane, β-SiAlON membrane and TiO2 membrane, in many cases have high chemical stability, enhanced mechanical strength and high thermal stability, which is of great value in some special separation process.7,8

Ceramic ultrafiltration membrane with large pore size and high flux is relatively mature. Nevertheless, low fouling resistance and loose functional layer are still two great challenges to further application of the ceramic membranes. Therefore, an increasing number of studies have been carried out to fabricate ceramic NF membranes with small pore size and hydrophilic surface. In order to change the permselectivity and surface properties of the ceramic membranes, a lot of materials such as hydrophilic polymer, graphene oxide (GO), MXene and nanoparticles have been used to modify the surface of the polymer or ceramic membranes.9–13 Chen et al. utilized in situ chemical deposition method to tune pore size and fabricate TiO2 multi-channel nanofiltration membrane with ceramic ultrafiltration substrate. After modification, the average membrane pore radius was changed from 2.4 nm to 0.9 nm.14 MnO2 nanoparticles were incorporated in the ceramic membranes and the prepared membrane showed high removal efficiency of p-chloronitrobenzene.15 Li et al. used the technique of atomic layer deposition (ALD) to tune the pore size of ceramic membranes. With the increase of ALD cycles, the pore size decreased with a gradient porous structure.16 However, the modification technique often needs high energy consumption or complicated preparation process. Polymer coating with high hydrophilicity is common for polymeric composite NF membrane preparation. But polymer/ceramic composite membranes are rarely prepared by depositing polymer on ceramic membranes because of low compatibility between polymer and ceramic materials. There is still great challenge in preparing defect-free polymer/ceramic composite membranes.

Dopamine can spontaneously self-polymerize to form bioinspired polydopamine (PDA) under mild alkaline condition. Recently, PDA has attracted great interest for its wide utilization in surface modification because it can work as a glue on different substrates such as polymer, ceramic and metal.17–19 The PDA coating on polysulfone UF membrane can reduce fouling in oily water filtration because it can enhance surface hydrophilicity.20 Furthermore, PDA coating has plenty of functional groups which can act as a platform for the post-functionalization. And the excellent hydrophilicity of PDA is meaningful for the antifouling performance of PDA membrane. Mazinani et al. used PDA as the coating material to prepare PDA/poly(vinylidene fluoride) NF membrane. The composite membrane showed a pure water flux of 14 L (m2 h bar)−1 with a MWCO of 550 Da.21 Zhao et al. reported the fabrication of solvent stable nanofiltration membrane based on an interpenetrating polymer network of dopamine and polybenzimidazole, which needed about 3 days to achieve in situ polymerization of PDA.22 Recent developments have focused on the challenge of speeding up the deposition time. Alammar et al. used PDA as the coating material to prepare NF membrane with high solvent resistance. In order to improve the membrane forming efficiency, 5 mM NaIO4 was added and the deposition time can be shorted to 1 h.23 Zhang et al. used CuSO4/H2O2 and (NH4)2S2O8 to accelerate the reaction. The optimized reaction time was 45 min.24 Gao et al. used PDA coating on the ceramic membrane as a platform to induce the metallization of Ag ions into Ag nanoparticles with CuSO4/H2O2 as a trigger. The PDA coating time was shortened from 16 h to 50 min.25. Zhao et al. used asymmetric Al2O3 tubular membranes as supports to prepare PDA/ceramic composite membrane. The formed composite membrane crosslinked with glutaraldehyde showed significant improvement in the rejection of salt solutions and excellent thermal resistance with a flux about 4 L (m2 h bar)−1. However, the base ceramic membrane with fine pore size of 5 nm was needed in this experiment. Also, it needed 2 h to form the polymer coating and additional crosslinking.26 Recently, KMnO4 was used as a water-soluble oxidant during PDA coating, which can reduce coating time obviously in a single reaction process and endow glass materials with dense functional layer and durable UV shielding property.27 This process route has important inspiration to prepare polymer/ceramic composite membrane efficiently.

Herein, we propose a very easy process to modify the ceramic membrane surface with PDA which is of great significance to promote the industrial application of ceramic NF membrane. The base ceramic membrane was firstly immersed in the PDA solution for several minutes to form skin layer and then dried in oven for 10 min to form dense functional layer. In this design, the KMnO4 acts as a trigger to accelerate the polymerization, which decreases the functional layer forming time obviously. The PDA/ceramic composite membrane showed dense and thin skin layer with excellent permselectivity.

2 Experimental

2.1 Materials and instruments

Flat sheet Al2O3 ceramic membrane (Jiangxi Bocent Advanced Ceramic, average pore diameter: 0.1 μm) with inner flow channel and dense outer layer has an active membrane area of 842 cm2. It was used as supporting membrane to prepare the composite membrane while PDA was used as the functional layer material. Dopamine hydrochloride (AR, Aladdin, shanghai, China) was used as the monomer of PDA. Polyethyleneimine (PEI, MW: 10[thin space (1/6-em)]000 Da), KMnO4, Na2CO3 and Congo red used in the experiments were all analytical purity grade (AR, Aladdin, shanghai, China) without further purification. The performance of the flat-sheet composite membrane was tested with a dead-end filtration set-up. UV-Vis Spectrometer (752N, Shanghai Youke, shanghai, China) was used to characterize the dye concentration while the conductivity meter (DDS-11A, Leici, shanghai, China) was used to test the salt concentration.

2.2 Membrane preparation

In this experiment, PDA functional layer was prepared on the top surface of ceramic membrane by oxidative self-polymerization of dopamine. Firstly, 1 g Na2CO3 and 0.2 g KMnO4 were added into 1 L deionized water with strong stirring, and then 2 g dopamine hydrochloride (DA) was added into the solution and the purple solution turned quickly into black during 20 min stirring. The clean ceramic membrane was immersed into the solution with fixed time to adsorb polymer and form PDA membrane. Then the membrane was taken out and dried at 80 °C for 10 min in oven. At last, the product was cleaned with deionized water for further characterization. For the membrane with PEI, the procedures are all the same except a certain amount of PEI was added in the solution during stirring.

2.3 Membrane characterization

The morphology and element composition of the membrane were analyzed by SEM equipped with Energy Dispersive X-ray (EDX) (FEI Nova NanoSEM 450, USA). The samples were sputtered with gold before detection to observe the images of the membranes at the voltage of 15 kV. The elemental composition of membrane surface was analyzed with Al K Alpha Gun with a spot size of 500 μm and 10 scans by XPS (ESCALAB™ 250Xi, ThermoFisher).

The performances including flux (F) and rejection (R) of the membrane were characterized by a vacuum membrane filtration set-up. In order to decrease the concentration polarization, an aeration system was fixed above the membrane surface. The membranes were tested under 0.1 MPa at room temperature. The concentration of Congo red solution was fixed 0.05 g L−1. The permeation flux (F) was calculated as follows:

 
image file: d2ra06959h-t1.tif(1)
where W is the total volume of the water or solution permeated during filtration process; A is the valid membrane area; and t is the operation time. Rejection, R, was calculated using the following equation:
 
image file: d2ra06959h-t2.tif(2)
where Cp and Cf are the concentrations of the permeate solution and the feed solution, respectively. All the experiments on flux and rejection were tested on three membranes with the average data shown in the paper. For the fouling resistance experiment, the data was tested with one membrane without repetition.

3 Results and discussion

3.1 Effect of reaction time on the morphology and performance of composite membranes

The morphologies of ceramic membrane and composite membrane were analyzed by SEM with a magnification of 20[thin space (1/6-em)]000×. The top surface morphologies of the membranes were shown in Fig. 1. The base ceramic membrane showed Al2O3 particles and large pores in the top surface. When PDA was introduced in the membrane surface at room temperature, part of the membrane was covered by polymer. With the increase of reaction time, denser membrane surface was observed. When the reaction time was increased to 15 min, the surface of the membrane was completely covered by nanoflakes. However, the density of the nanoflakes is not sufficient to plug the pores of the base membrane. So PDA provides a facile and fast method for the surface modification of ceramic membranes with the existence of oxidant at room temperature. The catechol moieties are used to anchor the ceramic membrane and self-polymerization formed highly cross-linked PDA coatings.
image file: d2ra06959h-f1.tif
Fig. 1 Effect of reaction time on the top surface morphologies of composite membrane ((a) base ceramic membrane; (b) 5 min; (c) 10 min; (d) 15 min).

In order to demonstrate the success of the membrane forming in the top surface, XPS test was performed to verify the success membrane formation on the support membrane. Fig. 2 showed the electron region of the XPS spectra of the membrane surface and high resolution spectra of C 1s and N 1s. The peaks at 284.8 eV and 399 eV were attributable to C 1s and N 1s, which were generated from PDA membrane. The N1s spectrum of the membrane can be fitted into two peaks centered at 398.4 and 399.8 eV, which corresponded to pyridinic- and pyrrolic-like nitrogen, respectively. The small peaks at 74 eV and 120 eV were indexed to Al 2p and Al 2s because the functional layer was very thin and Al2O3 support membrane was detected. The sharp peak located at 531 eV was attributable to O 1s, which may came from Al2O3 and PDA. The tiny peak located at 641 eV was attributable to Mn 2p. As part of KMnO4 was reduced by dopamine hydrochloride, MnOx was formed on the membrane surface, and the peak value of Mn element was very small.


image file: d2ra06959h-f2.tif
Fig. 2 XPS spectra of the composite membrane. (a) Survey spectrum, (b) detailed spectrum of C 1s, (c) detailed spectrum of N 1s.

The pure water flux of the composite membranes showed in Fig. 3 was tested at 0.1 MPa and room temperature. The base membrane showed the highest flux about 524 L (m2 h bar)−1. With the increase of reaction time, the membrane flux decreased gradually because of the increase of mass transfer resistance. When the reaction time was 15 min, the membrane flux declined to 335 L m−2 h−1. The result was in accordance with the SEM images of the membrane top surface. When the reaction time was 10 min, the composite membrane showed reasonable flux and morphology. So the reaction time was fixed at 10 min in the following experiments.


image file: d2ra06959h-f3.tif
Fig. 3 Effect of reaction time on the flux of composite membrane.

3.2 Effect of reaction temperature on the membrane morphology

In order to investigate the effect of reaction temperature on the morphology of the composite membrane, the ceramic substrate membrane was placed in a constant temperature water bath containing 2 g L−1 dopamine solution. The results showed that the temperature had a significant effect on the membrane formation. As shown in Fig. 4, the surface of the ceramic membrane was covered by PDA and had some small bumps. At 20 °C, some very small cracks appeared on the upper surface of the composite membrane, which limited the selectivity of the composite membrane. When the reaction temperature was raised to 40 °C, the ceramic membrane was covered with a dense PDA coating. The membrane surface was very smooth without any cracks or pores observed even if the SEM image was magnified 50[thin space (1/6-em)]000 times. When further heated to 60 °C, long cracks appeared on the surface of the membrane, and the alumina particles of the ceramic base membrane were revealed. The cross-section morphologies of the composite membrane were shown in Fig. 5. It is evident that the dense skin layer of the membrane gradually was thickened from 28.6 nm to 60.7 nm. Higher temperatures led to thicker layers but larger defects, which may be caused by low compatibility and big difference in thermal expansion coefficient between the polymer and ceramic materials.
image file: d2ra06959h-f4.tif
Fig. 4 Effect of reaction temperature on the top surface morphologies of composite membrane with different magnifications ((a) and (b) 20 °C; (c) and (d) 40 °C; (e) and (f) 60 °C).

image file: d2ra06959h-f5.tif
Fig. 5 Effect of reaction temperature on the cross-section morphologies of composite membrane with different magnifications ((a) and (b) 20 °C; (c) and (d) 40 °C; (e) and (f) 60 °C).

3.3 Effect of PEI content on the membrane morphology and performance

The composite membrane with 2 g L−1 PEI was analyzed by SEM as shown in Fig. 6. The top surface of the composite membrane was very dense without pores detected at the high magnification of 50[thin space (1/6-em)]000. The ultrathin PDA layer was detected on the Al2O3 base membrane with a thickness about 43 nm. With the aid of PEI, the membrane without defects was obtained, which is critical to the high rejection of the composite membrane. And the functional layer is ultrathin which is beneficial to the membrane flux. Meanwhile, the elemental mapping images in Fig. 7 showed that N is evenly distributed within the membrane surface with an atomic ratio of 5% which confirmed the effective coating of PDA. The atoms of Al (37%) and O (47%) were observed in the membrane surface because of the Al2O3 base membrane. Trace element Mn was also found because KMnO4 was reduced to Manganese oxide and which was stuck to the surface of the membrane by PDA.
image file: d2ra06959h-f6.tif
Fig. 6 Morphologies of the composite membrane with PEI ((a) top surface; (b) cross-section).

image file: d2ra06959h-f7.tif
Fig. 7 Top surface mapping of the composite membrane with PEI (atomic percentages are shown in the figure).

The effect of PEI content on the performance was studied with different weight ratios of PEI in the PDA solution. As shown in Fig. 8, the blank ceramic membrane has a rejection of 47.7% to Congo red with high water flux of 524 L m−2 h−1 at 0.1 MPa. When PDA was coated on the ceramic membrane, the dye rejection was improved to 80.4% dye while membrane flux was decreased to 429 L (m2 h bar)−1. The large pores in the membrane may be blocked by PDA, resulting in a smaller mean pore size which was in accordance with the SEM images. PEI has a significant effect on the membrane properties. When PEI content was increased to 2 g L−1, the membrane showed a 99.7% rejection to Congo red with a reasonable flux of 165 L m−2 h−1. The high dye rejection is due to the very dense layer of the membrane.


image file: d2ra06959h-f8.tif
Fig. 8 Effect of PEI concentration on the performance of the composite membrane (tested with 50 mg L−1 Congo red at 0.1 MPa. Blank, base ceramic membrane).

As shown in Table 1, PDA coating was time consuming, although the composite membrane showed good permselectivity.21 In order to improve the membrane forming rate, oxidants such as CuSO4/H2O2 was used which can accelerate the reaction obviously. The reaction time was shortened to 45 min.24–26 The surface modification of ceramic membrane with inorganic particles usually required higher temperature and longer time.28 In our work, the modification time was shortened to 10 min and the modification temperature was very low (40 °C), which is very conducive to the production of composite membrane. At the same time, the composite membranes prepared in our work showed high rejection and high flux to Congo red.

Table 1 Comparison of the membrane preparation and performance
Membrane Oxidants Temperature Time Rejection Permeate Flux References
PDA/PVDF Air 25 °C 24 h 94% RB5 (991 Da) 14 LMH bar−1 21
PDA/PAN CuSO4/H2O2 60 °C 45 min 90% PEG 1000 10.1 LMH bar−1 24
PDA/Al2O3 CuSO4/H2O2 25 °C 50 min Oil 1926 LMH bar−1 25
PDA/PEI/Al2O3 25 °C 2 h 91% MgCl2 4 LMH bar−1 26
TiO2/Al2O3 950 °C 2 h Oil 300 LMH bar−1 28
PDA/Al2O3 KMnO4 40 °C 10 min 80.4% Congo red (697 Da) 429 LMH bar−1 This work
PDA/PEI/Al2O3 KMnO4 40 °C 10 min 99.7% Congo red (697 Da) 165 LMH bar−1 This work


The fouling resistance of the composite membrane was also tested by continuous operation with Congo red solution for 180 min. The control experiment was conducted with base ceramic membrane at the same condition. As shown in Fig. 9, the flux of base membrane decreased quickly during the first 30 min, and the membrane flux decreased to 24% of the initial flux after 180 min operation. When PDA and PEI were introduced in the functional layer, the membrane flux also decreased with extension of operation time because dye molecule also adsorbed into the polymer layer. However, the flux decrease velocity was slower obviously compared with the membrane without modification. After 180 min operation, the flux was decreased to 57% and 55% of initial flux, respectively. For the PDA/ceramic membrane without PEI also showed good fouling resistance because PDA is also hydrophilic material. The membrane flux was declined to the 49% of initial flux after continuous 3 h operation.


image file: d2ra06959h-f9.tif
Fig. 9 Effect of PEI concentration on the fouling resistance of the composite membrane (tested with 50 mg L−1 Congo red solution; M1, blank ceramic membrane; M2, composite membrane prepared with PDA and 1 g L−1 PEI; M3, composite membrane prepared with PDA and 2 g L−1 PEI; M4, composite membrane prepared with only PDA).

4 Conclusions

In this study, the PDA/Al2O3 composite membrane was successfully prepared on the Al2O3 flat membrane with pore size of 0.1 μm. The composite membrane was prepared with dip-coating method and PDA worked as the functional layer material. KMnO4 was introduced to accelerate the rate of polymerization and membrane forming. The membrane preparation time was reduced to 10 min, which significantly improved the preparation efficiency. The functional layer of the composite membrane was very dense and thin, with a thickness of about 43 nm. The results of XPS and EDX mapping confirmed that the PDA functional layer was successfully prepared on the Al2O3 ceramic membrane, because not only Al and O elements but also N element were observed in the composite membrane surface. The rejection to Congo red of the PDA/ceramic composite membrane was significantly improved from 47.7% to 80.4% while the flux was decreased from 524 to 429 L m−2 h−1. When 2 g L−1 PEI were added in the coating solution, the rejection was increased to 99.7% while the flux decreased to 165 L m−2 h−1. After continuous operation of 180 min, the Al2O3 ceramic membrane without modification showed only 24% of initial flux. In contrast, the flux of PDA/ceramic composite membrane with 2 g L−1 PEI decreased to 55% of initial flux. The PDA/ceramic composite membrane without PEI also showed 49% of initial flux. The results confirmed the formation of a hydrophilic coating on the surface of the ceramic membrane.

Data availability statement

The data presented in this study are available on request from the corresponding author.

Author contributions

Conceptualization, R. H. and H. W.; methodology, R. H.; investigation, C. W. and G. Y.; writing—review and editing, R. H.; all authors have read and agreed to the published version of the manuscript.

Conflicts of interest

The authors declare no conflict of interest.

Acknowledgements

This research was funded by Jiangxi Province Double Thousand Talents Plan (jxsq2020101049) and Jiangxi Provincial Natural Science Foundation of China (20202BABL203021).

References

  1. L. Joseph, B. M. Jun and M. Jang, et al., Removal of contaminants of emerging concern by metal-organic framework nanoadsorbents: a review, Chem. Eng. J., 2019, 369, 928–946 CrossRef CAS.
  2. R. Han, Y. Zhang and Y. Xie, Application of Mn3O4 nanowires in the dye waste water treatment at room temperature, Sep. Purif. Technol., 2020, 234, 116119 CrossRef CAS.
  3. L. Zhou, H. Li and R. Han, Synthesis of self-assembled hierarchical AlPO-34 microspheres by using an ionic liquid and its application in heavy metal removal, R. Soc. Open Sci., 2021, 8, 201322 CrossRef CAS PubMed.
  4. T. Wang, H. Qiblawey, E. Sivaniah and A. Mohammadian, Novel methodology for facile fabrication of nanofiltration membranes based on nucleophilic nature of polydopamine, J. Membr. Sci., 2016, 511, 65–75 CrossRef CAS.
  5. M. Abdalla, M. Nasser, A. K. Fard, H. Qiblawey, A. Benamor and S. Judd, Impact of combined oil-in-water emulsions and particulate suspensions on ceramic membrane fouling and permeability recovery, Sep. Purif. Technol., 2019, 212, 215–222 CrossRef CAS.
  6. J. M. Gohil and P. Ray, A review on semi-aromatic polyamide TFC membranes prepared by interfacial polymerization: potential for water treatment and desalination, Sep. Purif. Technol., 2017, 181, 159–182 CrossRef CAS.
  7. D. Lu, T. Zhang and J. Ma, Ceramic membrane fouling during ultrafiltration of oil/water emulsions: roles played by stabilization surfactants of oil droplets, Environ. Sci. Technol., 2015, 49, 4235–4244 CrossRef CAS PubMed.
  8. Z. Zhong, W. Xing and B. Zhang, Fabrication of ceramic membranes with controllable surface roughness and their applications in oil/water separation, Ceram. Int., 2013, 39, 4355–4361 CrossRef CAS.
  9. R. Han, K. Wu and L. Xu, Facile Preparation of Loose P84 Copolyimide/GO Composite Membrane with Excellent Selectivity and Solvent Resistance, Polymers, 2022, 14, 1353 CrossRef CAS PubMed.
  10. M. Naguib, V. N. Mochalin, M. W. Barsoum and Y. Gogotsi, MXenes: a new family of two-dimensional materials, Adv. Mater., 2014, 26, 982 CrossRef.
  11. L. Kang, L. Zhao, S. Yao and C. Duan, A new architecture of super-hydrophilic β-SiAlON/graphene oxide ceramic membrane for enhanced anti-fouling and separation of water/oil emulsion, Ceram. Int., 2019, 45, 16717–16721 CrossRef CAS.
  12. P. Daraei, S. S. Madaeni, N. Ghaemi, M. A. Khadivi, B. Astinchap and R. Moradian, Enhancing antifouling capability of PES membrane via mixing with various types of polymer modified multi-walled carbon nanotube, J. Membr. Sci., 2013, 444, 184–191 CrossRef CAS.
  13. R. L. Han, Y. L. Xie, X. F. Ma, D. Teng, S. H. Zhang and X. G. Jian, Preparation of poly(2,4,6-triaminopyrimidine-TMC)/P84 composite nanofiltration membrane with enhanced chlorine resistance and solvent resistance, J. Chem. Technol. Biotechnol., 2019, 94, 2838–2843 CrossRef CAS.
  14. X. Chen, Y. Zhang, J. Tang, M. Qiu, K. Fu and Y. Fan, Novel pore size tuning method for the fabrication of ceramic multi-channel nanofiltration membrane, J. Membr. Sci., 2018, 552, 77–85 CrossRef CAS.
  15. X. Cheng, H. Liang, F. Qu, A. Ding, H. Chang, B. Liu, X. Tang, D. Wu and G. Li, Fabrication of Mn oxide incorporated ceramic membranes for membrane fouling control and enhanced catalytic ozonation of p-chloronitrobenzene, Chem. Eng. J., 2017, 308, 1010–1020 CrossRef CAS.
  16. F. Li, Y. Yang, Y. Fan, W. Xing and Y. Wang, Modification of ceramic membranes for pore structure tailoring: the atomic layer deposition route, J. Membr. Sci., 2012, 397–398, 17–23 CrossRef CAS.
  17. D. J. Miller, D. R. Paul and B. D. Freeman, An improved method for surface modification of porous water purification membranes, Polymer, 2014, 55, 1375–1383 CrossRef CAS.
  18. D. J. Miller, S. Kasemset, L. Wang, D. R. Paul and B. D. Freeman, Constant flux crossflow filtration evaluation of surface-modified fouling-resistant membranes, J. Membr. Sci., 2014, 452, 171–183 CrossRef CAS.
  19. B. D. McCloskey, H. B. Park, H. Ju, B. W. Rowe, D. J. Miller and B. D. Freeman, A bioinspired fouling-resistant surface modification for water purification membranes, J. Membr. Sci., 2012, 413–414, 82–90 CrossRef CAS.
  20. S. Kasemset, L. Wang, Z. He, D. J. Miller, A. Kirschner, B. D. Freeman and M. M. Sharma, Influence of polydopamine deposition conditions on hydraulic permeability, sieving coefficients, pore size and pore size distribution for a polysulfone ultrafiltration membrane, J. Membr. Sci., 2017, 522, 100–115 CrossRef CAS.
  21. S. Mazinani, A. Al-Shimmery, Y. M. John Chew and D. Mattia, 3D printed nanofiltration composite membranes with reduced concentration polarisation, J. Membr. Sci., 2022, 644, 120137 CrossRef CAS.
  22. D. Zhao, J. F. Kim, G. Ignacz, P. Pogany, Y. M. Lee and G. Szekely, Bio-Inspired Robust Membranes Nanoengineered from Interpenetrating Polymer Networks of Polybenzimidazole/Polydopamine, ACS Nano, 2019, 13, 125–133 CrossRef CAS PubMed.
  23. A. Alammar, R. Hardian and G. Szekely, Upcycling agricultural waste into membranes: from date seed biomass to oil and solvent resistant nanofiltration, Green Chem., 2022, 24, 365 RSC.
  24. C. Zhang, Y. Lv, W. Qiu, A. He and Z. Xu, Polydopamine Coatings with Nanopores for Versatile Molecular Separation, ACS Appl. Mater. Interfaces, 2017, 9, 14437–14444 CrossRef CAS PubMed.
  25. N. Gao and Z.-K. Xu, Ceramic membranes with mussel-inspired and nanostructured coatings for water-in-oil emulsions separation, Sep. Purif. Technol., 2019, 212, 737–746 CrossRef CAS.
  26. C. Zhao, X. Yu, X. Da, M. Qiu, X. Chen and Y. Fan, Fabrication of a charged PDA/PEI/Al2O3 composite nanofiltration membrane for desalination at high temperatures, Sep. Purif. Technol., 2021, 263, 118388 CrossRef CAS.
  27. T. Z. Mohammadizadeh, R. Amir, B. Mojtaba and A. Mohsen, Polydopamine surface modification with UV-shielding effect using KMnO4 as an efficient oxidizing agent, Colloids Surf., A, 2018, 559, 68–73 CrossRef.
  28. Q. Chang, J. Zhou, Y. Wang, J. Liang, X. Zhang, S. Cerneaux, X. Wang, Z. Zhu and Y. Dong, Application of ceramic microfiltration membrane modified by nano-TiO2 coating in separation of a stable oil-in-water emulsion, J. Membr. Sci., 2014, 456, 128–133 CrossRef CAS.

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