 Open Access Article
 Open Access Article
Mengxiao Sun†
, 
Geng Tan†, 
Zilong Dou, 
Jian Song, 
Xueting Qu, 
Yuyang Tian * and 
Guangshan Zhu
* and 
Guangshan Zhu *
*
Key Laboratory of Polyoxometalate and Reticular Material Chemistry of Ministry of Education, Faculty of Chemistry, Northeast Normal University, Changchun, Jilin 130024, China. E-mail: tianyy100@nenu.edu.cn; zhugs@nenu.edu.cn
First published on 22nd October 2025
To address the challenges of global water scarcity and high energy consumption for water purification, nanofiltration by porous membranes provides a promising solution. The demand for precise pore modulation and enhanced stability in membranes renders porous organic frameworks (POFs) promising alternatives to polymeric membranes, as their intrinsic porosity can help overcome the typical selectivity-permeability trade-off. A key current goal is to synthesise POF membranes at size scales suitable for practical applications. Herein, a cost-effective and facile synthesis method is proposed to synthesize membranes comprising porous aromatic frameworks (PAFs), which are a class of porous frameworks with carbon-carbon-linked aromatic building units. Specifically, bulk PAF sheets are prepared on glass substrates by establishing noncovalent interactions between substrate hydroxyl groups and functional PAFs. A large number of PAF bulk sheets are directly synthesized on common substrates such as glass slides and silica wafers. These bulk sheets are readily assembled into membranes by spin coating. The obtained PAF membranes exhibit unprecedented nanofiltration performance, with water permeability up to 700 L m−2 h−1 MPa−1 and rejection above 99% for the organic dye Congo Red. This surface-assisted synthesis and assembly of PAF membranes represent a step forward in the fabrication of porous organic separating membranes.
The preparation of continuous PAF membranes overcomes the limitations of crystalline microporous membranes in terms of performance regulation and stability, and therefore, they are considered potential candidates for separating membranes.27 Although a few PAF membranes have been synthesized by covalent bonding on smooth surfaces with anchoring sites, studies have shown that it is still a challenge to achieve growth control for PAFs from powder compounds to a two-dimensional layered morphology. This is mainly because PAFs are insoluble frameworks due to the high irreversibility of the non-dynamic chemical bond formation process.28 In previous work, we successfully synthesized a continuous PAF membrane for gas separation using a surface-initiated strategy.9 Covalent bonds were formed between PAF membranes and substrate surfaces. The key to the success of the surface-initiated strategy is modifying an active site that covalently binds to PAFs on the substrate surface, and multi-step reactions and modifications are required to achieve specific and high-density modification of the active sites. The complex surface initiation process is currently the main impediment to the successful synthesis of continuous PAF membranes on a large scale. To solve this problem, there is an urgent need to develop a universally applicable, simple and cost-effective method for PAF membrane preparation, in contrast to the previously used surface-initiated strategy.
Glass substrates and other oxide surfaces are commonly used in laboratories and production factories, and direct growth of PAF membranes at these surfaces would be attractive for the fabrication process. Considering the surface chemistry, there are abundant hydroxyl groups at the surfaces of glass and other oxide substrates. Unlike establishing covalent bonds on substrate surfaces, it would be an efficient and simple synthetic method to prepare PAF films by constructing noncovalent interactions directly with hydroxyl functional groups. Herein, PAF bulk sheets on the millimeter scale are directly synthesized on general substrates like glass slides, silica wafers, or even the inner walls of glass containers without extra modifications. It is found that noncovalent interactions between PAFs and substrates play an important role in the successful growth and morphology control for flake-like PAFs. Building units of PAFs with hydroxyl groups are necessary, and the results indicate that the interaction between PAF building units and hydroxyl-containing substrates contributes to the simple and large-scale synthesis of PAF bulk sheets, and finally leads to a series of large-size continuous PAF membranes as a result of their assembly.
The self-assembled PAF membranes exhibit unprecedented water permeability as high as 700 L m−2 h−1 MPa−1 and over 99% retention for the organic dye Congo Red (CR). In this study, noncovalent interactions are crucial to trigger the surface growth, which reduces the manufacturing cost of PAF membranes, improves the yield of layered PAFs, and solves the major problems that otherwise hinder the development of low-cost, large-size separating membranes. The study provides important concepts and strategies for the preparation of a wide range of PAF membranes with high performance, and promotes the development of continuous PAF membranes with functional tunability for water purification.
The PAF-80 bulk sheets were successfully synthesized on the glass surface, as observed by the color change of the transparent glass slides. They were then stripped from the surface of the glass substrate by simple ultrasonication (Fig. 2b), and the size and shape of the PAF bulk sheets were derived from the glass substrate. The synthetic process was monitored using Fourier-transform infrared (FT-IR) spectroscopy. The changes in the spectra showed the successful growth of PAF-80 on the glass slides, evidenced by the disappearance of the vibration at 3282 cm−1 originating from the terminal alkyne group in TEB, and the disappearance of the vibration at 1068 cm−1 from the C–Br bond in TBBT. At the same time, the low-intensity bands at 2200 cm−1 for the synthesized PAF-80 were assigned to the stretching vibration modes of the alkyne (C![[triple bond, length as m-dash]](https://www.rsc.org/images/entities/char_e002.gif) C) moieties.29 All these results indicated the synthesis of PAF-80 in the expected way. The wide infrared band at 3440 cm−1 could be attributed to a tensile vibration of the hydroxyl group (–OH), indicating that the hydroxyl group remained after the coupling reaction. The main characteristic peaks of PAF-80 powder and PAF-80 sheets were consistent, thus demonstrating the successful synthesis of PAF-80 bulk sheets (Fig. 2c and S1). The integrity of the PAF-80 bulk sheets on the substrate was characterized using scanning electron microscopy (SEM), and no significant cracks or pore defects were observed (Fig. 2d and S2). Energy dispersive spectroscopy (EDS) elemental mapping of PAF-80 sheets on the glass substrate showed a continuous and homogeneous carbon distribution (Fig. S3). The microscopic morphology of the PAF-80 sheets was characterized by transmission electron microscopy (TEM), and the sheets showed two-dimensional silk-like texture with stacked layers (Fig. 2e and S4). Atomic force microscopy (AFM) was used to evaluate the thickness and roughness of the PAF-80 sheets. The thickness changes of the PAF-80 sheets at different time intervals were also monitored by AFM to investigate the growing progress (Fig. 3). The AFM images showed that a continuous layer was formed on the surface of the substrates after 6 hours, with a thickness of about 70 nm, and the surface of the layer was smooth and particle-free (Fig. 3a). After 24 h, the thickness of the layer increased to 85 nm, and a small number of accumulated particles could be observed atop the layer (Fig. 3c). After 96 h of reaction, the thickness of the layer reached 112 nm, and a significantly rough surface was observed, which may be formed by the accumulation of PAF particles on the sheet surface (Fig. 3f). The growing thickness of the layer linearly increased over time, suggesting an epitaxial growing mechanism for the formation of an amorphous layer on a flat surface (Fig. S5). Usually, PAFs from aromatic building units show extreme hydrophobicity, which results in diminished water permeation across their pores. Herein, the water compatibility of the PAF-80 sheets was monitored by water contact angle testing. As the growth time increased, the water contact angle gradually became smaller, demonstrating that the PAF-80 sheets became more hydrophilic due to the presence of hydroxyl groups. The hydrophilic sheets were promising to enhance the water permeability (Fig. S6). X-ray photoelectron spectroscopy (XPS) results indicated that the surface of the PAF-80 bulk sheet is exposed to abundant hydroxyl groups (Fig. S7).
C) moieties.29 All these results indicated the synthesis of PAF-80 in the expected way. The wide infrared band at 3440 cm−1 could be attributed to a tensile vibration of the hydroxyl group (–OH), indicating that the hydroxyl group remained after the coupling reaction. The main characteristic peaks of PAF-80 powder and PAF-80 sheets were consistent, thus demonstrating the successful synthesis of PAF-80 bulk sheets (Fig. 2c and S1). The integrity of the PAF-80 bulk sheets on the substrate was characterized using scanning electron microscopy (SEM), and no significant cracks or pore defects were observed (Fig. 2d and S2). Energy dispersive spectroscopy (EDS) elemental mapping of PAF-80 sheets on the glass substrate showed a continuous and homogeneous carbon distribution (Fig. S3). The microscopic morphology of the PAF-80 sheets was characterized by transmission electron microscopy (TEM), and the sheets showed two-dimensional silk-like texture with stacked layers (Fig. 2e and S4). Atomic force microscopy (AFM) was used to evaluate the thickness and roughness of the PAF-80 sheets. The thickness changes of the PAF-80 sheets at different time intervals were also monitored by AFM to investigate the growing progress (Fig. 3). The AFM images showed that a continuous layer was formed on the surface of the substrates after 6 hours, with a thickness of about 70 nm, and the surface of the layer was smooth and particle-free (Fig. 3a). After 24 h, the thickness of the layer increased to 85 nm, and a small number of accumulated particles could be observed atop the layer (Fig. 3c). After 96 h of reaction, the thickness of the layer reached 112 nm, and a significantly rough surface was observed, which may be formed by the accumulation of PAF particles on the sheet surface (Fig. 3f). The growing thickness of the layer linearly increased over time, suggesting an epitaxial growing mechanism for the formation of an amorphous layer on a flat surface (Fig. S5). Usually, PAFs from aromatic building units show extreme hydrophobicity, which results in diminished water permeation across their pores. Herein, the water compatibility of the PAF-80 sheets was monitored by water contact angle testing. As the growth time increased, the water contact angle gradually became smaller, demonstrating that the PAF-80 sheets became more hydrophilic due to the presence of hydroxyl groups. The hydrophilic sheets were promising to enhance the water permeability (Fig. S6). X-ray photoelectron spectroscopy (XPS) results indicated that the surface of the PAF-80 bulk sheet is exposed to abundant hydroxyl groups (Fig. S7).
During the synthesis process of PAF-80 sheets with different growth times, it was found that PAF powder was also present in the reaction system but could be removed, while the membranes were attached to the surface of the substrates and even the reaction vials (Fig. S8). In this case, the attached bulk sheets and free PAF powder were readily isolated by washing. Following ultrasonication, the large-area membranes were successfully detached from the substrates and transferred to the vial (Fig. S9–11). We propose that this phenomenon can be attributed to supramolecular interactions driven by surface interface chemistry. Specifically, hydroxyl groups on the glass substrates likely formed noncovalent bonds with the structural units of the PAF-80 bulk sheets. Although individual supramolecular interactions were relatively weak, their collective synergistic effect enabled the growth of extensive PAF-80 bulk sheets along the substrates.
A homemade pressure-assisted filtration device (Fig. S25) was used to test the flux of pure water through the PAF membranes and the separation performance of the membranes for aqueous solutions of Congo Red (CR). The concentration of the aqueous CR solution was 100 mg L−1, and the working pressure of the device could be adjusted using a pressure gauge. Before the formal test, the continuous PAF membranes were pressurized with pure water at 0.2 MPa for 2 h to ensure stable permeability, and then the pure water flux and dye separation performance of the continuous PAF membrane were tested under 0.1 MPa conditions, and the subsequent permeate was collected after discarding the initial 1 h permeate. Determination of the feed and osmotic concentration of the aqueous CR solution was carried out using a UV-vis spectrophotometer. Two important parameters for evaluating the performance of PAF membranes were permeability (P) and rejection rate (R), determined by the following equations:
After obtaining the PAF bulk sheets, the nanofiltration performance of four types of PAF bulk sheets was first tested and evaluated. The separation results are shown in Fig. S27 and Table S2. To fully achieve nanofiltration membranes for water purification, PAF-80 bulk sheets were dispersed in a chlorobenzene solution of PMMA and prepared as large-size membranes using the spin-coating method (Fig. 5a and b). SEM confirmed the continuity of the PAF-80 membranes and the uniform distribution of the elements (Fig. 5c, d and S28). The thickness of the PAF-80 membrane was increased very little, maintaining 113 nm (Fig. S28).
The nanofiltration performance of PAF-80 membranes for aqueous CR solutions was tested and evaluated (Fig. 5e–g). The water flux through the PAF-80 membrane can be stabilized above 700 L m−2 h−1 MPa−1, and the retention rate of CR reached 99.9%. Moreover, even after five nanofiltration cycles, the membrane can still achieve a permeation flux of over 700 L m−2 h−1 MPa−1 and a rejection rate of 99.9% (Table S3). The separation performances of the PAF-81 membrane, PAF-82 membrane and PAF-18 membrane were investigated under the same testing conditions. The separation results are shown in Fig. S29 and Table S4. The zeta potential results indicate that PAF-80 possesses a negative surface charge, while CR is also negatively charged. Therefore, no electrostatic interaction exists between PAF-80 and CR (Fig. S30). The high retention was caused by the size sieving effect of the porous aromatic sheets. As calculated by NLDFT simulation according to the nitrogen adsorption isotherm, the pore size of PAF-80 was centered at 0.52 nm (Fig. S31), which is smaller than the molecular dimension of CR.33 Combining the analysis of the PAF-80 membrane skeleton structures with experimental results reveals that PAF-80 membranes contain hydroxyl functional groups, which readily allow adjustment of membrane surface properties to achieve high water flux and high CR molecular rejection. PAF membranes are expected to achieve the separation of CR molecules in wastewater with the actual water flux and good rejection rate (Table S5).
![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) :
:![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) 1 vol) of tetrakis(triphenylphosphine) palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) was added to the mixture. TEB (0.1 mmol, 15 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
1 vol) of tetrakis(triphenylphosphine) palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) was added to the mixture. TEB (0.1 mmol, 15 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) :
:![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) 1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. DTB (0.1 mmol, 18.9 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. DTB (0.1 mmol, 18.9 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) :
:![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) 1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. TEPB (0.1 mmol, 37.85 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction mixture was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. TEPB (0.1 mmol, 37.85 mg) and TBBT (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction mixture was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) :
:![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif) 1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. TEPM (0.1 mmol, 31.24 mg), and monomer 2 (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
1 vol). Tetrakis(triphenylphosphine)-palladium (0.012 mmol, 13.8 mg) and CuI (0.012 mmol, 2.3 mg) were added to the mixture and activated at 100 °C for 1 h. TEPM (0.1 mmol, 31.24 mg), and monomer 2 (0.1 mmol, 36.3 mg) were added to the reaction system, and the operating environment was all nitrogen. The reaction was carried out at 100 °C for 48 h. At the end, the reaction was cooled to room temperature, and the glass slide was washed with trichloromethane and anhydrous methanol.
| Footnote | 
| † These authors contributed equally to this work. | 
| This journal is © The Royal Society of Chemistry 2025 |