Next Article in Journal
Finned Tubular Air Gap Membrane Distillation
Previous Article in Journal
Red Fruit Juice Concentration by Osmotic Distillation: Optimization of Operating Conditions by Response Surface Methodology
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Effect of Interlayer Construction on TFC Nanofiltration Membrane Performance: A Review from Materials Perspective

School of Civil Engineering and Architecture, Chuzhou University, Chuzhou 239000, China
*
Authors to whom correspondence should be addressed.
Membranes 2023, 13(5), 497; https://doi.org/10.3390/membranes13050497
Submission received: 17 April 2023 / Revised: 1 May 2023 / Accepted: 6 May 2023 / Published: 8 May 2023

Abstract

:
Polyamide (PA) thin-film composite (TFC) nanofiltration (NF) membranes, which are extensively utilized in seawater desalination and water purification, are limited by the upper bounds of permeability-selectivity. Recently, constructing an interlayer between the porous substrate and the PA layer has been considered a promising approach, as it may resolve the trade-off between permeability and selectivity, which is ubiquitous in NF membranes. The progress in interlayer technology has enabled the precise control of the interfacial polymerization (IP) process, which regulates the structure and performance of TFC NF membranes, resulting in a thin, dense, and defect-free PA selective layer. This review presents a summary of the latest developments in TFC NF membranes based on various interlayer materials. By drawing from existing literature, the structure and performance of new TFC NF membranes using different interlayer materials, such as organic interlayers (polyphenols, ion polymers, polymer organic acids, and other organic materials) and nanomaterial interlayers (nanoparticles, one-dimensional nanomaterials, and two-dimensional nanomaterials), are systematically reviewed and compared. Additionally, this paper proposes the perspectives of interlayer-based TFC NF membranes and the efforts required in the future. This review provides a comprehensive understanding and valuable guidance for the rational design of advanced NF membranes mediated by interlayers for seawater desalination and water purification.

1. Introduction

Nanofiltration (NF) membranes are a type of pressure-driven membrane that has the ability to intercept low-molecular-weight organic molecules and multivalent ions. These membranes have found widespread application in seawater desalination, drinking water purification, and wastewater treatment. The most commonly used commercial NF membranes are polyamide (PA) thin-film composite (TFC) membranes prepared by interfacial polymerization (IP), owing to their ease of processing, mature technology, and low cost. However, the trade-off between permeability and selectivity of TFC NF membranes has hindered the improvement of water permeability and solute retention rate simultaneously [1,2,3,4]. As a result, larger membrane areas and higher operating pressures are required for practical applications, which increases construction and operation costs. Hence, developing NF membranes with both high permeability and high retention is crucial for cost reduction.
PA TFC membranes have undergone tremendous development as the most successful commercialized product since the introduction of the concept of interfacial polymerization (IP) by Morgan in the early 1980s [5]. Despite the passage of nearly four decades, IP remains the foremost industrial technology for producing commercialized membranes. The typical IP process entails impregnating porous polymer support with a diamine aqueous solution, followed by exposure to a trimesoyl chloride organic solution. As the solubility of trimesoyl chloride in water is negligible, and the solubility of diamine is moderate in organic solvents [6], the polymerization reaction mainly occurs at the organic phase at the water-oil interface, where the diamine monomer diffuses from the water phase into the organic phase and rapidly reacts with the trimesoyl chloride. The resulting Janus reaction zone leads to the formation of an asymmetric PA nanofilm (with a total thickness of approximately 100 nm), where the amine and carboxyl groups are enriched on the water-phase and organic-phase sides, respectively. This gives rise to nanoscale heterogeneity in the PA nanofilm, which has been extensively discussed in studies by Freger et al. [7,8]. They concluded that the PA nanofilm features a negatively charged top layer, followed by a more densely packed positively charged sublayer.
PA TFC NF membranes mainly consist of a nonwoven fabric, a support layer, and a PA separation layer. The ultra-thin PA separation layer plays a crucial role in determining the flux and separation performance of the NF membrane. An ideal NF membrane should exhibit excellent water permeability and high removal rates of organic matter, multivalent salts, and other pollutants [9]. The thickness and crosslinking degree of the PA separation layer influence the overall separation performance of the TFC membrane. The traditional PA separation layer is approximately 100 nm, resulting in significant water transport resistance [10]. Therefore, it is necessary to reduce the thickness of the PA separation layer and increase the crosslinking degree to prepare high-performance NF membranes [11].
According to the classical theory of membrane separation and mass transfer, the permeability of a membrane is negatively correlated with the thickness of its selective layer [12]. Therefore, the thinner the selective layer, the higher the permeability [13]. The ultra-thinning of composite NF membranes is, in fact, the ultra-thinning of the PA separation layer. TFC NF membranes prepared by the IP method belong to diffusion-controlled reactions because of the rapid reaction rate of IP and the significant influence of the diffusion process of the water-phase monomer to the oil phase on the separation layer structure. Freger [7] summarized the kinetic model of the formation of the PA separation layer, and the thickness (δ) calculation formula is as follows:
δ     LD κ C a f a + C b f b 1 / 3
where L is the interface diffusion boundary layer thickness, D is the diffusion rate of the amine monomer to the water-oil interface, κ is the reaction rate constant between the two monomers, Ca is the local concentration of amine monomer, fa is the functional-coefficient of the amine monomer, Cb is the local concentration of acyl chloride monomer, and fb is the functional-coefficient of the acyl chloride monomer. By reducing the diffusion rate of amine monomers to the water-oil interface and increasing the local concentration of amine monomers, the thickness of the PA separation layer can be reduced.
To date, studies have shown that the physical and chemical properties of porous substrates significantly affect the formation of PA separation layers, presenting two challenges for the creation of ultra-thin and dense skin layers [11,14,15]. The first challenge is that existing porous substrates typically exhibit poor hydrophilicity and low porosity, leading to insufficient penetration of amine monomers on the substrate and resulting in defects in the formation of PA separation layers [16]. The second challenge is that the IP rate constant generated by the reaction of PIP and TMC is greater than 104 L mol−1 s−1, making it difficult to kinetically control the IP process, which is not conducive to the formation of thin and dense PA separation layers [7,17].
In recent years, it has been demonstrated that the incorporation of an interlayer prior to the IP process on porous substrates is an effective approach for modifying the substrate [18,19]. The interlayer introduction induces a gutter effect, which enhances the transport efficiency of TFC NF membranes, leading to an increase in the membrane flux [20,21]. Furthermore, the interlayer can act as a reservoir for amine monomers, thereby elevating their concentration and regulating their release. The reaction between the amine and acyl chloride monomers on the interlayer generates an ultra-thin, defect-free, and dense PA active layer, which results in simultaneous enhancements of both the water permeability and salt rejection rate of the membrane [16,22]. This technology was first pioneered by Livingston et al. using a new type of composite substrate comprising a porous hydrophilic Cd(OH)2 nano strands sacrificial layer and the original UF substrate combined together, which has superior amine monomer storage capacity and controls the release of amine monomers to a certain extent. On the composite substrate, a 10 nm thick defect-free PA skin layer was formed by IP, which significantly improved solvent permeability while maintaining excellent salt retention capability. Since this groundbreaking work, numerous studies have focused on various interlayer materials, such as organic coatings and nanomaterials, to modify porous substrates and prepare TFC NF membranes with high permeability and high salt rejection properties. The TFC NF membranes with interlayers are referred to as TFCi in this article, while TFC0 refers to TFC NF membranes without interlayers.
Although the interlayer structure plays a crucial role, there is still a lack of a review of the influence of the interlayer structure on the performance of TFC NF membranes from a materials perspective. This article reviews the knowledge of TFC NF membranes based on various interlayer materials and provides useful information for researchers involved in developing high-performance TFC NF membranes.

2. Organic Interlayers

Organic hydrophilic polymers have abundant functional groups [23,24], which can easily be used to construct a uniform and continuous interlayer on a porous substrate. The interaction between the organic interlayer and the reactive monomer or the porous substrate can not only regulate the structure and performance of TFC PA NF membranes but also enhance the stability between the PA layer and the porous substrate [19,25,26,27]. So far, organic polymers used to construct interlayers mainly include polyphenols, ionic polymers, polymeric organic acid, and other types of organic matter.

2.1. Polyphenols

Polyphenols are natural compounds synthesized by plants that possess chemical characteristics similar to phenolic substances and exhibit strong antioxidant properties [28]. Polyphenolic chemistry for surface modification has gained significant attention in membrane science due to its simplicity and cost-effectiveness [29]. Polyphenols can also serve as an interlayer deposited on the support layer to enhance its hydrophilicity, which is beneficial in the manufacture of NF membranes [19,30].
Tannic acid (TA), a type of plant polyphenol, is widely used due to its rich terminal hydroxyl groups, including catechol and caramel alcohol structures, and broad sources [31]. Yang et al. [32] fabricated TFC PA NF membranes on TA-Fe nano-scaffolds. The TA-Fe nanomaterials exhibited improved absorption of amine monomers and served as a platform for the controlled release of the absorbed molecules. Additionally, the presence of a TA-Fe interlayer in the substrate resulted in smaller surface pores, which prevented the penetration of PA into the pores of the original substrate. The resulting TFCi membrane has a water permeability of 19.6 ± 0.5 L m2− h−1 bar−1, which is one order of magnitude higher than that of the control TFC membrane (2.2 ± 0.3 L m2− h−1 bar−1). At the same time, it increased the rejection of salts and the selectivity of divalent to monovalent ions (e.g., NaCl/MgSO4). However, the coordination bonds formed by TA-Fe are unstable in acidic environments, which limits its application. Zhao et al. [31] aimed to enhance the stability of the interlayer and achieved this by conducting a rapid in-situ coupling reaction between TA and diazonium salts (DDS), resulting in the construction of a stable diazo-based interlayer on a polysulfone (PSF) UF substrate. Compared to traditional NF membranes, the optimized new NF membrane’s water permeability was improved by 2.71 times.
In addition to TA, polyphenol-polyethyleneimine (PEI) coatings have also been used as interlayer materials. PEI possesses numerous primary amine groups, which can impart a significant positive charge to the interlayer, thereby increasing the surface potential of the NF membrane [33]. Additionally, PEI can form uniform nanoscale aggregates with polyphenols, which enhances interlayer stability and hydrophilicity [25,33]. For example, Zhai et al. [25] deposited large cyclic polyphenol molecules Noria-PEI onto a PSF UF substrate, where they underwent a Schiff base reaction to form covalent bonds and obtain a stable and uniform interlayer composed of a homogeneous nanoscale adhesive aggregate. The resulting Noria-PEI layer, positively charged, and the negatively charged PA separation layer endow the NF membrane with excellent rejection capabilities against divalent cations and anions. The optimized membrane exhibits a permeated flux of approximately 28 L m2− h−1 bar−1 and rejection rates exceeding 96.0% for Na2SO4, MgSO4, MgCl2, and CaCl2. Inspired by this study, 5,5′,6,6′-tetrahydroxy-3,3,3′,3′-tetramethyl-1,1′-spirobisindane(TTSBI)-PEI [34] and catechol-PEI [33] have also been employed as interlayers to fabricate NF membranes with exceptional properties.
In addition to its co-deposition with PEI to form an interlayer, catechol can also be employed in combination with sodium periodate (SP) to prepare an interlayer. In a recent study, Tian et al. [35] demonstrated the preparation of an environmentally friendly polycarboxylic interlayer by mixing catechol and SP. Catechol, a polyphenolic compound, is susceptible to oxidation to form active o-quinones. Under the initiation of SP, these o-quinones can undergo phenolic polymerization and covalently polymerize with carboxyl groups. The introduction of carboxyl groups makes the interlayer hydrophilic, which can store more PIP molecules and provide a more uniform platform for IP, facilitating the formation of a thin and dense PA active layer. In comparison with traditional membranes, the modified TFC membrane has a 1.7-fold increase in permeability while maintaining a high rejection rate for Na2SO4 (98.42 ± 1.2%).
The interlayer of polyphenol has been extensively studied, yet the precise function and corresponding mechanisms leading to enhanced separation performance in TFCi NF membranes remain largely unknown. Yang et al. [20] developed a TFCi PA NF membrane with a polydopamine (PDA) interlayer. The optimal TFCi membrane flux was nearly an order of magnitude higher than that of the control TFC NF membrane. Additionally, the TFCi membrane exhibited efficient retention of inorganic salts and small organic molecules. Detailed mechanistic studies revealed that the membrane’s separation performance was enhanced through both the direct “gutter” effect of the PDA interlayer and its indirect influence on the PA layer, with the “gutter” effect exerting a more dominant role.

2.2. Ionic Polymers

In recent years, ion-polymer has also been used as an interlayer. The class of ionic polymers includes anionic polymers, cationic polymers, and zwitterionic polymers.
Hu et al. [36] introduced anionic polymer Poly(sodium 4-styrenesulfonate) (PSS) and a metal ion (Ca2+) complex interlayer on a PSF UF substrate to prepare a high-performance TFC NF membrane. The PSS-Ca2+ interlayer served as a nano scaffold, creating a more uniform IP platform that facilitated the formation of thinner and defect-free PA layers. As a macromolecular additive, PSS induced a diffusion-driven instability of the IP process, leading to the formation of a wrinkled PA layer with an increased surface area. This results in TFCi membranes that have four times the permeability (up to 22.15 ± 1.14 L m−2 h−1 bar−1) compared to traditional TFC0 membranes while still maintaining competitive rejection of Na2SO4. Deng et al. [37] used self-assembly to deposit anionic polymer sulfonated polyetherketone with cardo groups (SPEK-C) onto positively charged cadmium hydroxide (Cd(OH)2) nano strand, creating a highly permeable SPEK-C mesoporous interlayer. This interlayer not only enables the storage of a large number of water monomers but also generates electrostatic interactions with them, thereby temporarily slowing down their diffusion into the organic phase. The resulting PA NF membrane demonstrates excellent permeability and long-term operational stability.
In a recent study, Zhu et al. [38] incorporated a cationic polymer, quaternized crosslinked microgels (PNI6), onto a negatively charged hydrolyzed polyacrylonitrile (PAN) UF substrate to fabricate a TFC PA NF membrane. By introducing positively charged PNI6 microgels as the interlayer, the hydrophilicity of the product is improved, and the NF membrane surface becomes positively charged. Song et al. [39] provide another comparable instance where they have incorporated a cationic polymer, namely poly(allylamine hydrochloride) (PAH), onto a PSF UF substrate to fabricate an NF membrane with exceptional properties. The self-assembled network of strongly charged and highly hydrophilic ion aggregates exhibits a strong attraction to water amine monomers and temporarily disrupts their diffusion by applying a heterogeneous energy barrier to the organic phase, which then copolymerizes with the acyl chloride monomer. This instability in the diffusion driving force triggers the formation of internal voids on the back of the PA NF membrane.
In addition to anionic and cationic polymers, zwitterionic polymers have also been used in the preparation of NF membranes as interlayers. Song et al. [40] utilized a zwitterionic polymer, P[MPC-co-AEMA], consisting of 2-methacryloyloxyethyl phosphorylcholine (MPC) and 2-amino-ethyl methacrylate hydrochloride (AEMA), as an interlayer for the fabrication of a TFC NF membrane (Figure 1). The resulting membrane has an ultra-high water permeability of 20.4 L m2− h−1 bar−1 (almost three times higher than the original PA membrane) and enhances the rejection of inorganic salts (the rejection rate for Na2SO4 is 96.8%). This was attributed to the abundant amine monomers in the P[MPC-co-AEMA] interlayer, which induced diffusion-driven instability, resulting in membrane sealing and inhibition of its growth. As a result, an ultra-thin PA NF membrane with a thickness of 12 nm, enhanced surface area, and enhanced crosslinking with a ridged surface structure was formed.
The data in Table 1 show that anionic polymers are the most effective interlayers for preparing TFC NF membranes, followed by zwitterionic polymers, and finally cationic polymers. This could be attributed to the fact that anionic polymers as interlayers can adsorb more quinine solution. According to Freger’s kinetics [7], an increase in amine monomer concentration is beneficial for producing thinner membranes and improving membrane flux. Additionally, anionic polymers as interlayers facilitate the preparation of membranes with a stronger negative charge, which is beneficial for intercepting Na2SO4. The adsorption capacity of zwitterionic and cationic polymers for PIP decreases in sequence, resulting in a corresponding decrease in the separation performance of TFC NF membranes prepared using these polymers.

2.3. Polymeric Organic Acid

Polymeric organic acids, due to their abundant carboxyl and hydroxyl groups, exhibit good hydrophilicity and are also used as interlayers. For example, Liu et al. [41] utilized hyaluronic acid (HA) as an interlayer material to fabricate a novel type of TFC NF membrane. The hydrogen bonds formed between HA and amine monomers act to inhibit the mass transfer of PIP, leading to the construction of a PA layer with enhanced electronegativity, reduced thickness, a wrinkled structure, and increased cross-linking degree. The resulting TFC NF membrane exhibited exceptional water permeability (29.53 L m2− h−1 bar−1) and achieved high removal rates for Na2SO4 (94.90%) and perfluorohexane sulfonic acid (93.4%). Wang et al. [42] conducted a comparable investigation whereby they deposited poly(caffeic acid) (PCA) onto the surface of PAN UF membranes, constructing a composite interlayer and ultimately fabricating high-performance TFC NF membranes.

2.4. Other Organic Interlayers

Researchers also used other types of organic materials to study the interlayer. For example, Zhu et al. [27] incorporated polyvinyl alcohol (PVA) as an interlayer on a PES UF substrate to fabricate TFC NF membranes. The interlayer provided a large surface area, high hydrophilicity, and high porosity, resulting in an NF membrane with a thickness of only 9.6 nm. The resulting membrane achieved an ultra-high water permeability of 31.4 L m2− h−1 bar−1 and a high Na2SO4 rejection rate of 99.4%. In addition, the membrane showed good stability and scalability in pilot studies. Lan et al. [43] fabricated high-performance TFC NF membranes by constructing a hydrophilic and uniform gelatin (GT) interlayer on a PSF substrate. This interlayer not only influenced the diffusion rate of PIP to form a thin PA layer but also provided additional channels for water diffusion, significantly enhancing the permeability of the NF membrane. The permeability of the TFCi NF membrane was approximately 2.5 times higher than that of the control membrane while also achieving a high Na2SO4 removal rate. Liu et al. [44] prepared a novel TFC NF membrane with a poly (amidoxime) (PAO) organic interlayer. The PAO interlayer significantly enhanced the surface hydrophilicity of the PES substrate, and PAO could bind with PIP through hydrogen bonding and Lewis acid-base interactions, reducing the diffusion rate of PIP and causing instability at the oil-water interface during the IP process. This led to the formation of NF membranes with regular nanorod-like Turing structures and a thin PA layer thickness of only 18.2 nm. The optimized TFC NF membrane showed a permeating flux of up to 25.2 L m2− h−1 bar−1 and a rejection rate of over 99% for Na2SO4. Chen et al. [45] developed a novel interfacial coating interlayer on a PSF UF substrate using glutaraldehyde (GA) cross-linked PEI and dextran nanoparticles (DNPs) (Figure 2). DNPs were semi-encapsulated within the PEI coating, while the exposed nanoparticles were embedded in the PA layer to form an interfacial channel during IP. The pure water permeation rate of the interlayer TFC NF membrane was 31.33 L m2− h−1 bar−1, about four times that of the original membrane. Additionally, the NF membrane showed a significant improvement in the retention rate of various divalent salts, with the Na2SO4 retention rate exceeding 99%.
Through the comprehensive analysis of structural parameters and filtration performance of TFC NF membranes with organic material-interlayer (Table 1), comparative studies were conducted. Results showed that the polyphenol interlayer had been extensively studied in the development of novel TFC NF membranes compared to interlayers such as ionic polymers and polymeric organic acid. In order to improve the stability of TFC NF membranes, crosslinking agents such as PEI and GA are commonly employed to react with other organic materials to form the interlayer, while metal ions are used to chelate with other organic materials to create intermediate layers. Moreover, various porous substrates, including PES, PSF, and PAN, have been utilized in TFC NF membranes with organic interlayers, indicating the efficacy of the organic interlayer regardless of the substrate. As shown in Table 1, there is no clear correlation between monomer concentration and PA thickness, highlighting the significance of the organic interlayer in forming an ideal thin PA layer. After the incorporation of the organic interlayer, the membrane flux range of all TFCi NF membranes was between 10.1–31.4 L m2− h−1 bar−1, and the retention rate range for Na2SO4 was between 93.4% and 99.4%. The Na2SO4 rejection performance of organic interlayer TFC NF membranes is equivalent to that of commercial NF membranes. Although the flux of these membranes is considerably higher than that of typical commercial NF membranes, further improvement is challenging. This is possibly due to the fact that while organic polymers can increase membrane flux by reducing the thickness of the PA layer and increasing its wrinkled structure, they may also block substrate pores and increase membrane resistance, ultimately hindering further flux improvement.

3. Nanomaterial Interlayer

3.1. Nanoparticles

Nanoparticles (NPs) are tiny particles ranging in size from 1 to 100 nanometers. They can be divided into three main types based on their composition: inorganic NPs, organic NPs, and organic-inorganic hybrid NPs.

3.1.1. Inorganic NPs

SiO2 is an inorganic nanoparticle material that exhibits notable hydrophilicity and chemical stability, making it a suitable interlayer material with good interfacial affinity and chemical reactivity. In order to enhance the stability of SiO2 on a PSF substrate, Song et al. [46] have employed an in-situ method to fabricate a siliconization interlayer (Figure 3). This process involves the hydrolysis of the silicate ester precursor in an aqueous environment to generate silanol, which subsequently reacts with the chloride acyl group located on the surface of the PSF membrane, forming a uniform siliconization layer. This technique can circumvent the issue of nanoparticle agglomeration and sedimentation during subsequent processing, thereby improving the stability of SiO2. The above-mentioned method only improves the stability of SiO2 on the substrate and does not mention the stability between SiO2 and the PA layer. To enhance the stability of SiO2 between the substrate and the PA layer concurrently, Wang et al. [47] incorporated PDA into SiO2. PDA can tightly bind to the SiO2 microsphere surface via a self-polymerization reaction, leading to the formation of a stable PDA@SiO2 interlayer between the PA layer and the poly(m-phenylene isophthalamide) (PMIA) substrate. This interlayer can augment the adhesion and compatibility between the PA layer and the PMIA substrate, consequently elevating the stability and mechanical strength of the composite NF membrane. Furthermore, PDA can create a cross-linking structure with PA molecules through hydrogen bonding, which further enhances the stability of the PA layer. The optimal membrane exhibits exceptionally high permeability, boasting a pure water flux of 31.37 ± 1.06 L m2− h−1 bar−1, which is three times higher than that of traditional PA NF membranes, and a Na2SO4 rejection rate of up to 97.0%.

3.1.2. Organic NPs

Covalent organic framework (COF), a type of organic nanoparticle material, possesses exceptional hydrophilicity and polymer affinity, along with ordered pores and adjustable pore size, which provide molecular sieving channels suitable for interlayers in NF membrane preparation. Han et al. [48] synthesized a COF (TPB-DMTP-COF) with uniform pore size for the NF membrane, serving as an interlayer material to regulate the physicochemical properties of the PA membrane. COFs, displaying affinity and hydrophilicity, can not only prevent non-selective interface voids but also decrease the diffusion rate of PIP towards the water/n-hexane interface by means of hydrogen bonding. The water permeability of the resulting TFCi membrane is significantly enhanced, nearly four times that of the unmodified PA membrane.

3.1.3. Organic-Inorganic NPs

The metal-organic framework (MOF) is an organic-inorganic nanoparticle material composed of metal ions/clusters and organic scaffolds with highly controllable pore size and surface area, as well as an adjustable pore structure. These characteristics enable it to accelerate solvent transport by separating polymer chains or through its inherent pore structure. Additionally, the presence of organic ligands in MOFs improves their compatibility with the PA layer, reducing defect formation and enhancing interface stability. These features make MOFs a good interlayer material. Zhao et al. [49] introduced a zeolitic imidazolate framework-8 (ZIF-8) interlayer between a PA layer and a microporous poly(ether sulfone) (PES) membrane. Adding PSS to a ZIF-8 water solution containing Zn2+ can stabilize the ZIF-8 layer at the water/n-hexane interface and facilitate the uniform loading of ZIF-8 onto the substrate, effectively covering large pores. The surface of the PES membrane loaded with ZIF-8 becomes smoother and negatively charged, providing better conditions for IP to form a thin, loose, and defect-free TFC NF membrane. Additionally, the pure water permeability of the TFC membrane, containing a modified ZIF-8 interlayer, is twice that of the original TFC membrane.

3.2. One-Dimensional Nanomaterials

One-dimensional (1D) nanomaterials have the advantages of high porosity between materials, uniform pore size distribution, good hydrophilicity, and large surface charge, which can reduce the thickness of the PA layer, promote wrinkling morphology, and improve separation performance [16,50]. Therefore, 1D nanomaterials are suitable as interlayer materials for preparing NF membranes. The 1D nanomaterials are mainly divided into inorganic 1D nanomaterials and organic 1D nanomaterials.

3.2.1. Inorganic 1D Nanomaterials

In recent studies, several researchers have utilized inorganic 1D nanomaterials as interlayers to prepare highly efficient NF membranes. Karan et al. [14] achieved a breakthrough in the manufacture of ultrathin films by conducting IP on Cd(OH)2 nanowire layers. The resulting nanowire interlayer facilitated the storage of diamine solution and control of diamine monomer release, ultimately leading to the formation of an ultrathin, defect-free PA skin layer. However, the subsequent removal of Cd(OH)2 nanowires may compromise the composite strength between the PA layer and substrate surface, leading to increased complexity in the manufacturing process. From a practical standpoint, interlayers exhibiting chemical stability are more desirable.
Carbon nanotubes (CNTs) that have been functionalized with carboxylic acid groups can serve as a robust mechanical support and facilitate IP by absorbing and storing aqueous amino solutions, making them suitable as interlayer materials [16,21,51,52]. Nonetheless, the presence of weak interfacial interactions between CNTs and porous substrates can result in deleterious delamination during practical applications [16,29,53]. In order to enhance the stability between the carbon nanotube interlayer and porous substrate, various methods have been developed, such as coating CNTs with PDA, carboxylating multi-walled carbon nanotubes (MWCNTs), employing brush painting to disperse single-walled carbon nanotubes (SWCNTs), and using inkjet printing technology to prepare stable CNT interlayers. For example, Zhu et al. [54] developed a PDA-coated SWCNT (PDA/SWCNT) ultra-thin film as a support layer for the preparation of TFC NF membranes. The PDA/SWCNTs composite material has a high porosity, smooth surface, and excellent hydrophilic properties. PDA forms strong interaction forces between the substrate and the PA layer, increasing adhesion and improving the stability of the composite material. The resulting TFCi NF membrane showed exceptional performance with a permeate flux of 32 L m2− h−1 bar−1 and a 95.9% rejection rate for divalent ions. Wu et al. [16] conducted carboxylation of MWCNTs and utilized them as interlayers on the MF substrate to fabricate TFC NF membranes. The introduction of carboxylated MWCNTs can enhance the compatibility and adhesion between the interlayer and the substrate, leading to improved stability and performance of the TFC NF membrane. Gao et al. [51] employed a brush painting to disperse SWCNTs onto a polymer MF support, creating a network of SWCNTs as an interlayer. After subjecting the interlayers to soaking experiments for 30 days, all interlayers remained intact, and there was no peeling of SWCNT films from the underlying PES MF substrate. This confirms that brush painting is capable of producing interlayers with excellent chemical and mechanical stability. This approach enabled the formation of a 15-nm-thick PA layer, and the resulting TFCi NF exhibited an extremely high water permeation rate (~40 L m2− h−1 bar−1) and a rejection rate of 96.5% for Na2SO4. Park et al. [52] used inkjet printing technology to prepare stable SWCNT interlayers, which is because inkjet printing technology can achieve high precision, high speed, and reproducibility of deposition, thereby allowing the morphology and distribution of materials to be controlled at the nanoscale.
CNTs have been used as an interlayer to prepare a thin PA active layer with a thickness of nearly 10 nm, resulting in a membrane with higher permeability. Although this strategy of reducing the active layer is effective in improving membrane permeability, further improving membrane performance under this strategy is limited because preparing thinner defect-free active layers than the state-of-the-art will become very challenging. Without losing other features, increasing the effective permeable area of the ultra-thin PA active layer is a preferred approach. Wang et al. [55] created a PA active layer with a widely crumpled surface morphology by loading ZIF-8 NPs onto SWCNTs/PES scaffolds, with ZIF-8 as a sacrificial template, thereby creating a higher specific surface area and larger proportion of highly permeable PA skin layers. The resulting membrane exhibits high permeability of up to 53.5 L m2− h−1 bar−1 and a rejection rate of over 95% for Na2SO4.
According to Table 2, it can be observed that existing studies mainly use SWCNTs as the interlayer in the preparation of TFCi NF membranes, which show better performance compared to TFCi NF membranes prepared with MWCNTs as the interlayer. This is likely due to the smaller diameter of SWCNTs, which is advantageous for constructing a high-porosity interlayer that can store more PIP solution. According to Freger kinetics [7], an increase in the concentration of amine monomers is favorable for producing thinner membranes and improving membrane flux.
However, further research is necessary to understand how changes in interlayer structure and properties affect the formation and transport properties of PA. Recent studies have demonstrated the potential of tailoring interlayer properties to enhance the NF performance of TFC membranes. For example, Gong et al. [56] investigated the interlayer’s role in regulating the structure and performance of PA by introducing an SWCNT interlayer on a PSF MF substrate to prepare a TFC NF membrane. Through manipulation of the properties of the CNT interlayer, such as its thickness and surface pore size, the structure and performance of the PA active layer can be carefully tailored to improve its NF performance. The optimized TFCi NF membrane displayed a high rejection rate for divalent salts and dyes, as well as a highly pure water flux of approximately 21 L m2− h−1 bar−1. To explore the water transport mechanism in the TFCi NF membrane, Long et al. [21] analyzed an MWCNTs-incorporated TFCi membrane with an identical PA rejection layer but different interlayer thicknesses. It was observed that increasing the thickness of the MWCNTs interlayer improved the transport of water in the transverse direction, leading to an enhanced gutter effect, but also increased the hydraulic resistance in the normal direction. The optimal permeate flux was achieved at an interlayer thickness of 13.0 ± 0.7 L m2− h−1 bar−1. In this study, it was demonstrated that the TFCi NF membrane reduced membrane fouling and improved the reversibility of fouling compared to the control membrane without an interlayer, which could be ascribed to its more uniform water flux distribution.

3.2.2. Organic 1D Nanomaterials

Inorganic 1D nanomaterials, such as Cd(OH)2 [14] and CNTs [16,21,51,52,54,56], have been widely studied as interlayer materials for NF membranes, but their toxicity and poor compatibility with substrates and PA layers have been significant drawbacks [57,58]. To overcome the toxicity and compatibility issues associated with inorganic 1D nanomaterials, researchers have shifted their focus to developing hydrophilic, environmentally friendly, and non-toxic organic 1D nanomaterials as interlayer materials. Several recent studies have demonstrated the effectiveness of this approach, utilizing different organic nanomaterials as interlayers to achieve highly efficient NF membranes with impressive permeation rates and rejection capabilities. For example, Wang et al. [53] prepared NF membranes on a nanoporous substrate using a non-toxic and environmentally friendly cellulose nanocrystal interlayer. The high aspect ratio and hydrophilicity of the cellulose nanocrystals (CNCs) interlayer can store aqueous diamine monomers, slow down IP, and prepare thinner membranes. The constructed TFCi NF membrane exhibits an ultra-high permeation rate of up to 34 L m2− h−1 bar−1 and a rejection rate for Na2SO4 exceeding 97%. Similarly, Wang et al. [59] used highly hydrophilic and high surface area cellulose nanofibers (CNFs) as an interlayer to prepare TFC NF membranes. Compared to the control membrane, the water flux of the TFC NF membrane with interlayer CNFs was significantly increased by 270%, and the MgCl2 rejection rate was as high as 96.8%. Ji et al. [60] prepared a PA NF membrane on a UF substrate using a polyaniline nanofibers interlayer. The acid doping chemical reaction of polyaniline allows for tunable pore size and surface charge in the PA layer, which enhances ion separation. The optimized TFCi NF membrane demonstrates an ultra-high water permeation rate of 49.7 L m2− h−1 bar−1 and good retention for Na2SO4 and MgSO4, equivalent to 98.7% and 97.9% salt rejection, respectively. Similarly, Guo et al. [61] developed a sandwich-enhanced NF membrane using self-doped sulfonated polyaniline (SPANI) nanofibers as an interlayer. The degree of sulfonation in the interlayer was varied and increasing the sulfonation degree led to improved hydrophilicity and thinner, defect-free PA layers. The high sulfonation degree of SPANI also gives the TFCi membrane a high water permeation rate of up to 29.35 ± 1.23 L m2− h−1 bar−1 while retaining good rejection capability for Na2SO4 (98.92 ± 0.45%) and MgSO4 (96.21 ± 0.75%). However, the effect of combining the polyaniline interlayer with other chemical substances on the separation performance of TFCi NF membranes is still uncertain. Guo et al. [62] further investigated the impact of different types of alkaline solutions combined with polyaniline on the separation performance of TFCi NF membranes. The addition of NaHCO3 to the SPANI interlayer facilitated the formation of a thin and defect-free polyamide (PA) selective layer with a wrinkled and nanobubble dual morphology. The optimized TFCi NF membrane demonstrated a remarkable permeate flux of 35.35 L m−2 h−1 bar−1 and exhibited excellent rejection capabilities towards Na2SO4 (98.95 ± 0.29%) and MgSO4 (95.37%). Finally, Han et al. [63] used high porosity microporous organic nanotubes (MONs) as an interlayer and prepared a 15-nanometer-thick PA layer through IP (Figure 4). Prior to the IP reaction, a high-porosity and interconnected MON layer was added onto the membrane, which can form a turing structure PA membrane, increase the microporosity rate, and reduce thickness. The optimized TFCi NF membrane achieved a significant water permeability of 41.7 L m2− h−1 bar−1 under alkaline conditions (pH = 10) and high retention rates for boron (78.0%) and phosphorus (96.8%). Overall, the use of organic 1D nanomaterials as interlayers in NF membranes has shown great potential for improving their performance and efficiency, and these studies demonstrate the effectiveness of this approach in achieving highly efficient NF membranes for a variety of applications.

3.3. Two-Dimensional Nanomaterials

Two-dimensional (2D) nanomaterials possess high aspect ratios and significant lateral dimensions, rendering them conducive for covering large substrate pores with multiple stacked layers, thereby facilitating the attainment of a smooth and uniform surface that is indispensable for the IP process [64]. They can be divided into three main types based on their composition: inorganic 2D nanomaterials, organic 2D nanomaterials, and organic-inorganic 2D nanomaterials.

3.3.1. Inorganic 2D Nanomaterials

In recent years, researchers have employed inorganic 2D nanomaterials, such as graphene oxide (GO), MXene, and MoS2 as interlayers to develop NF membranes. GO nanosheets can achieve ultrafast water transport through nanochannels constructed from pristine graphene [65] thanks to their excellent mass transfer properties, such as ultra-low friction and ultra-high capillary effect. Moreover, GO nanosheets possess various oxygen-containing functional groups on their surfaces and edges, making them highly promising for use as interlayers in the fabrication of NF membranes. Nonetheless, GO does not undergo a chemical reaction or strong interaction with most substrates, such as PSF and polyether sulfone (PES), thereby making it difficult to attain stable adhesion, resulting in interlayer delamination during the filtration process [66,67]. Crosslinking with Pebax® 1657 and Toluene diisocyanate (TDI) can improve the stability of graphene oxide on PAN [68]. Inspired by this, to mitigate the instability of the GO interlayer, Zhang et al. [69] introduced PVA into GO, followed by crosslinking with GA. GA acts as a cross-linking agent, reacting with PVA to form a crosslinked structure, which fixes the GO nanosheets on the surface of the MF substrate. The resulting crosslinked structure enhances the stability and durability of the interlayer and improves the selectivity and permeability of the TFC NF membrane. Testing the anti-fouling performance of TFCi NF membrane using BSA-contaminated water samples as feed, it was found that TFCi NF membrane exhibited a lower flux decline compared to TFC0 NF membrane and had a higher flux recovery rate (FRR), indicating that TFCi NF membrane has superior anti-fouling performance. In addition, the stacking of GO nanosheets is also a barrier to its use as an interlayer because it increases the resistance of water passing through it. To reduce GO stacking, Wang et al. [70] inserted and crosslinked dispersed sub-5 nanometer silica NPs in situ in the GO interlayers. The hydrophilic NPs locally widened the interlayer channels, enhancing the permeability of solvents. This method has the potential to solve the aggregation problem of GO as an interlayer.
MXene, an inorganic 2D nanomaterial produced by selective etching, has attracted significant attention due to its hydrophilic end groups and mechanical flexibility [71]. Xu et al. [72] have fabricated a high-performance TFC NF membrane by utilizing the 2D sheet-like interlayer of MXene for IP. The MXene layer facilitated the absorption of active monomers, and higher amine monomer concentrations promoted self-sealing and self-termination of IP, resulting in thinner PA films with suppressed formation inside the substrate pores. The resulting TFCi NF membrane exhibited over 96% rejection of Na2SO4 and an excellent permeability of 45.7 L m2− h−1 bar−1, which was nearly 4.5 times that of the TFC0 NF membrane. However, the post-treatment process involving oxidants made the obtained high-performance PA NF membrane difficult to scale up, and the ultra-thin PA layer was transferred onto a PES support after dissolving the MXene layer, causing instability of PA membranes and deterioration of membrane performance [73,74]. In order to address this issue, Zhu et al. [75] prepared an efficient NF membrane by using MXene as an interlayer in an assisted IP process (Figure 5). The presence of the MXene layer increased the hydrophilicity of the original support and the adsorption of PIP, resulting in a faster IP reaction. The resulting MXene-interlayer NF membrane exhibited a rougher surface, higher hydrophilicity, higher electronegativity, and a denser skin layer. The MXene-interlayer NF membrane achieved an excellent water permeability of 27.8 ± 2.1 L m2− h−1 bar−1 while also achieving satisfactory selectivity, overcoming the trade-off between water permeability and salt selectivity.
The aforementioned examples illustrate the successful use of MXene as an interlayer material for the preparation of high-flux TFC NF membranes. This is because the introduction of the interlayer generates a gutter effect [20], which reduces the total resistance of the TFC nanofiltration membrane (sum of resistance in substrate, interlayer, and PA layer) [76], resulting in an increase in membrane flux. When MXene 2D nanosheets are used as interlayers, the excessive stacking of MXene functional groups and water molecules via hydrogen bonding decreases the interlayer spacing and elevates the transport resistance of water through the MXene interlayer itself. According to the resistance-in-series model of water transport resistance [77], the interlayer of an ideal TFCi membrane itself should have low transport resistance. Therefore, to address this issue, some researchers have investigated the insertion of other nanomaterials between MXene interlayers to regulate the interlayer spacing of the 2D channels, thus reducing the resistance of the MXene interlayer itself. For instance, Wang et al. [78] employed stacked MXene nanosheets as the interlayer and embedded Fe3O4 NPs as a sacrificial template to adjust the interlayer spacing. However, foreign insertions are inherently unstable for the long-term operation of the membrane. Alternatively, Fu et al. [79] successfully grew TiO2 in situ on MXene nanosheets via PMS oxidation. The TiO2 NPs can firmly bind to the MXene layer and enlarge the interlayer spacing, thereby mitigating the additional transport resistance of water molecules. Furthermore, the MXene-TiO2 heterostructure material exhibits a higher specific surface area than MXene [80,81], which facilitates the collection of more amide monomers to form a crumpled PA selective layer. This method has successfully produced high-performance NF membranes.
Recently, MoS2 has garnered significant attention as a promising inorganic 2D nanomaterial for membrane separation due to its exceptional mechanical stability, robust interlayer forces, and simple synthesis process. Cao et al. [76] fabricated a high-performance TFC NF membrane on a PSF substrate coated with MoS2. The MoS2-interlayer TFC NF membrane demonstrated superior roughness and crosslinking compared to the control group TFC NF membrane, owing to the enhanced confinement effect of interfacial degassing and the improved adsorption of amine monomers by the MoS2- interlayer. Additionally, the PA layer thickness of the MoS2-interlayer TFC membrane, which ranged from 60 to 85 nm, could be finely tuned by altering the thickness of the MoS2 interlayer. The optimized TFCi NF membrane exhibited a remarkable rejection rate of 96.8% for Na2SO4 and a desirable permeability of approximately 15.9 L m2− h−1 bar−1, which was approximately 2.4 times greater than that of the TFC0 NF membrane.

3.3.2. Organic 2D Nanomaterials

In addition to inorganic 2D nanomaterials, organic 2D nanomaterials have also attracted the interest of researchers. COFs are a class of organic 2D nanomaterials known for their remarkable porosity and strong covalent bonding within the all-organic skeleton [82]. Most COFs exhibit a highly ordered honeycomb-like structure with tunable pore sizes and layered structures [83], which makes them well-suited for selective small molecule separation through size exclusion. The exceptional water stability, high adsorption capacity, and well-defined structure make COFs promising candidates for storing amine monomers, thus making them suitable as interlayer materials. For example, Wu et al. utilized [84] a PDA-COF interlayer to mediate IP, resulting in ultra-thin composite membranes with enhanced NF performance. The PDA-COF interlayer with specific surface hydrophilicity and high porosity was able to control the adsorption/diffusion of amine monomers, leading to the formation of an ultra-thin and dense PA layer that reduced the thickness from 79 nm to 11 nm. The optimized TFCi NF membrane showed excellent desalination rate and dye rejection with outstanding water permeability of 20.7 L m2− h−1 bar−1. Additionally, the PDA-COF interlayer significantly enhanced the interfacial interaction between the PA layer and PAN substrate, providing the composite membrane with excellent structural stability. Another example is Yuan et al. [85] developed a composite substrate using COF nanosheets (CONs) deposited on an MF membrane through vacuum-assisted assembly, which allowed for the regulation of IP and produced a highly porous and super hydrophilic ultra-thin PA skin layer. The high porosity and superhydrophilicity of CONs in the composite substrate allowed for high storage capacity and uniform distribution of amine monomers, and by varying the loading amount of CONs, it was possible to regulate the monomer storage capacity, accelerate self-sealing and self-termination of IP, and produce ultra-thin PA skin layers ranging from 70 nm to below 10 nm. Moreover, due to the highly porous structure of CONs, the composite substrate exhibited almost no additional resistance to water transport. The optimized TFCi NF membrane exhibited outstanding water permeability of 53.55 L m2− h−1 bar−1, with a rejection rate of 94.3% for Na2SO4.

3.3.3. Inorganic-Organic 2D Nanomaterials

In a recent study, inorganic-organic 2D nanomaterials were also applied to prepare interlayer materials. For example, Cheng et al. [86] have developed a TFC NF membrane by incorporating MOFs as an interlayer in a PSF-based substrate. Through controlling the thickness of the MOFs (copper-tetrakis(4-carboxyphenyl) porphyrin, Cu-TCPP) interlayer, the structural parameters, such as effective filtration area, selective layer thickness and pore size, as well as the physicochemical properties of the membrane could be precisely adjusted. The experimental results indicate that the MOFs nanosheets with appropriate deposition density as interlayers could effectively increase the crosslinking degree by adsorbing PIP monomers while simultaneously reducing the thickness of the PA layer, resulting in enhanced intrinsic permeability. The optimized TFCi NF membrane demonstrates exceptional water permeability of 32.7 L m2− h−1 bar−1, as well as a high selectivity of 271.7 for NaCl/Na2SO4.
A thorough analysis was conducted to compare the structural parameters and filtration performance of TFC NF membranes with nano-material interlayers, as outlined in Table 2. The results demonstrate that 1D and 2D nanomaterial interlayers have been extensively studied for the development of new TFC NF membranes compared to nanoparticle interlayers. To enhance the stability of TFC NF membranes, PDA and nanomaterials are commonly combined. PDA is a bio-adhesive with a polyphenolic structure that interacts with various surfaces and has good biocompatibility and biodegradability. Therefore, the inclusion of PDA in NF membrane preparation improves the stability of TFC membranes. A variety of porous substrates such as PES, PSF, PMIA, PAN, Nylon, and PVDF have been used as substrates for nanomaterial interlayers. While both MF and UF substrates have been widely used for interlayer materials, NF membranes with ultrahigh permeate flux (>40 L m2− h−1 bar−1) have been obtained using MF substrates, which may be attributed to the high permeability of the MF substrate itself. Table 2 highlights that there is no obvious correlation between monomer concentration and PA thickness, emphasizing the critical role of nanomaterial interlayers in creating an optimal thin PA layer. Following the addition of nanomaterial interlayers, the flux range of all TFCi NF membranes falls between 9.48–53.55 L m2− h−1 bar−1, while the Na2SO4 retention range is between 91% and 99.9%. When compared to organic materials, nanomaterials exhibit higher permeability but equivalent salt rejection performance as interlayers. This may be due to the generally higher porosity of nanomaterials, which results in lower resistance as an interlayer in comparison to organic materials.
Table 2. Structure and performance of TFC NF membranes with nanomaterial interlayer.
Table 2. Structure and performance of TFC NF membranes with nanomaterial interlayer.
CategoryNanomaterial UsedPorous
Substrate
IP Condition
(Optimum)
Polyamide
Thickness (nm)
Water Flux
(L m−2 h−1 bar−1)
Salt
Rejection
Year
[Ref]
NPsZIF-8-PSSPES MF
substrate
(0.22 μm)
2 w/v% PIP/water,
0.13 w/v% TMC/n-hexane 1 min reaction
2359.691%
Na2SO4
2021
[49]
NPsSiO2PSF UF
substrate (Mw 30,000)
0.2 w/v% PIP/water,
0.1 w/v% TMC/n-hexane 30 s reaction
1514.598.7% Na2SO42021
[46]
NPsCOFPSF UF
substrate
0.1 wt% PIP/water,
0.1 wt% TMC/n-hexane
1 min reaction
4435.798.9% Na2SO42022
[48]
NPsPDA@SiO2PMIA substrate1 wt% PIP/water,
0.1 w/v% TMC/n-hexane 30 s reaction
20.931.3797% Na2SO42022
[47]
1DPDA/SWCNT
(5–30 μm × Φ < 2 nm)
PES MF
substrate
(0.4 μm)
0.025 w/v% PIP/water,
0.02 w/v% TMC/n-hexane 30 s reaction
123295.9% Na2SO42016
[54]
1DMWCNTs
(50 μm × Φ 8–15 nm)
PSF UF substrate
(Mw 30,000)
0.15 w/v% PIP/water,
0.02 w/v% TMC/n-hexane 30 s reaction
NA17.5795% Na2SO42016
[16]
1DCellulose nanocrystal (0.2–0.5 μm × Φ 20–50 nm)PES MF substrate
(0.22 μm)
0.5 mg/mL PIP/water
0.5 mg/mL TMC/n hexane 2 min reaction
453497.7% Na2SO42017
[53]
1DPDA@ZIF-8/PDA@SWCNTsPES MF
substrate
2.5 mg/mL PIP/water
2 mg/mL TMC/n-hexane 30 s reaction
NA53.595%
Na2SO4
2018
[55]
1DSWCNT
(5~30 μm ×
Φ 1–2 nm)
PES MF substrate
(0.45 μm)
0.125 w/v% PIP/water,
0.1 w/v% TMC/n-hexane 30 s reaction
154096.5% Na2SO42019
[51]
1DPDA/SWCNTs
(5–30 μm × Φ < 2 nm)
PES MF
substrate
(0.22 μm)
0.05 wt% PIP/water,
0.02 wt% TMC/n-hexane 30 s reaction
292198.5% Na2SO42019
[56]
1DSWCNT
(1~3 μm ×
Φ 1–2 nm)
PES MF substrate
(0.22 μm)
0.15 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
42.618.2497.88% Na2SO42021
[52]
1DPolyaniline nanofibersPES MF substrate
(0.45 μm)
1 w/v% PIP/water,
0.15 w/v% TMC/n-hexane 30 s reaction
1149.798.7% Na2SO42022
[60]
1Dsulfonated polyaniline nanofibers (0.58 μm × Φ 80 nm)PES MF substrate
(0.45 μm)
1 w/v% PIP/water,
0.15 w/v% TMC/n-hexane 30 s reaction
4829.3598.92% Na2SO42022
[61]
1DCellulose nanofibersPSF UF (Mw 50,000)0.3 w/v% PEI/water, 0.1 w/v% TMC/n-hexane 1min reaction105.413.396.8%MgCl22022
[59]
1DMWCNTsPES UF
substrate (Mw 20,000)
0.2 wt% PIP/water,
0.1 wt% TMC/n-hexane
2 min reaction
NA13NA2022
[21]
1DMicroporous organic nanotubesPSF substrate0.1 wt% PIP/water,
0.1 wt% TMC/n-hexane
1 min reaction
1541.798.7% Na2SO42022
[63]
1Dsulfonated polyanilinePES MF substrate
(0.45 μm)
1 wt% PIP/water,
0.15 wt% TMC/n-hexane 30 s reaction
4335.3598.95%
Na2SO4
2023
[62]
2DPDA-COF nanosheets (lateral size 60–130 nm)PAN UF
substrate
(Mw100,000)
0.1 w/v% PIP/water,
0.1 w/v% TMC/n-hexane 2 min reaction
1120.7193.4% Na2SO42019
[84]
2DCOF nanosheets
(lateral size 250 nm)
PES MF substrate
(0.10 μm)
0.15 wt% PIP/water,
0.15 wt% TMC/n-hexane 2 min reaction
753.5594.3% Na2SO42019
[85]
2DGO nanosheetsNylon MF substrate
(0.22 μm)
0.5 w/v% PIP/water,
0.5 w/v% TMC/n-hexane 2 min reaction
NA30.393.56% Na2SO42020
[87]
2DMXene nanosheetsPES UF substrate1 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
1527.899.9% Na2SO42021
[75]
2DMXene nanosheetsPES MF substrate
(0.22 μm)
0.2 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
2045.796% Na2SO42021
[72]
2DGO@PVA/GAPSF substrate0.3 wt% PIP/water,
0.06 wt% TMC/n-hexane 30 s reaction
1515.899.7% Na2SO42021
[69]
2DMOFs nanosheetsPES UF
substrate (Mw 20,000)
0.15 wt% PIP/water,
0.1 wt% TMC/n-hexane
1 min reaction
23.532.799.7% Na2SO42022
[86]
2DMoS2 (average
size of 2 μm)
PES UF substrate (Mw 150,000)1 wt% PIP/water,
0.15 wt% TMC/n-hexane 1 min reaction
72.715.996.8% Na2SO42022
[76]
2DTiO2 nanosheets
(lateral size 0.6–1.2 μm)/TiO2 NPs
PVDF MF substrate (0.45 μm)1 wt% PIP/water,
0.1 wt% TMC/n-hexane
15 s reaction
3036.3NA2023
[88]
2DMXene-TiO2PSF UF
substrate
(Mw 20,000)
0.75 wt% PIP/water,
0.038 wt% TMC/n-hexane 2 min reaction
30.2511.1098.29% MgSO42023
[79]
2DMXene Nanosheets/Fe3O4 NPsPSF UF
substrate
(Mw 20,000)
0.75 wt% PIP/water, 0.038 wt% TMC/n-hexane 2 min reaction229.48>97% MgSO42023
[78]

4. Comparison of Performance of TFCi NF Membranes

4.1. Comparison of Performance of TFCi NF Membranes with TFC0 NF Membranes

The present study provides a comprehensive review of the separation performance of interlayer TFC N membranes based on existing literature. The results indicate that the TFCi NF membrane exhibits significantly improved separation performance compared to the TFC0 NF membrane. Specifically, the average flux of the TFCi NF membrane increased from 9.92 L m2− h−1 bar−1 to 27.968 L m2− h−1 bar−1, representing an increase of 182%, as demonstrated in Figure 6a. Additionally, the average rejection rate of Na2SO4 for the TFCi NF membrane increased from 96.58% to 98.31%, as illustrated in Figure 6b, which suggests that the introduction of an interlayer has the potential to enhance flux without compromising the selectivity of the membrane. The observed improvements in separation performance can be attributed to the formation of a thin, dense, and crumpled TFC NF membrane after the incorporation of an interlayer. These findings demonstrate the promising potential of the interlayer strategy in overcoming the permeability-selectivity trade-offs of TFC membranes.

4.2. Comparison of Performance of TFCi NF Membranes Prepared Using Different Interlayer Materials

Figure 6 provides a comparison of the permeability and salt rejection rates of various materials. Specifically, Figure 6c demonstrates that the NF membrane incorporating a 1D nanomaterial as an interlayer exhibits the highest flux in terms of permeability. This can be attributed to the high aspect ratio, internal porosity, and uniform pore size distribution of 1D nanomaterials, which contribute to a reduction in PA layer thickness and the attainment of a crumpled morphology, ultimately resulting in higher permeability. Similarly, the NF membrane created with 2D nanomaterial as the interlayer also demonstrates a high flux due to the high surface area and unique physical and chemical properties of 2D nanomaterials, enabling them to establish a layered structure in two dimensions. This layered structure forms water channels that can be assembled into water channels by stacking nanosheets. However, 2D nanomaterials produce resistance to TFCi NF membranes, thus impeding membrane permeability improvement. By contrast, the organic interlayer exhibits the lowest flux because organic interlayers primarily consist of polymer materials with high molecular weight and large molecular size, leading to blockage of the NF membrane’s pore structure, thereby hampering the quantity and velocity of water molecules passing through the membrane. Additionally, the organic interlayer might form an extra resistance on the membrane’s surface and have adverse interactions with the active layer, reducing the NF membrane’s permeability. Figure 6d illustrates that the mean salt rejection rate of 2D materials is lower than that of 1D materials for sodium sulfate, which might be attributed to the fewer samples, the greater data fluctuations occur. Nevertheless, the maximum salt rejection rate of 2D materials surpasses that of 1D materials since 2D nanosheets inherently exhibit a blocking effect on salt. Finally, the NF membrane produced with an organic interlayer presents the highest mean salt rejection rate, potentially due to the abundant functional groups such as hydroxyl, carboxyl, and sulfonic acid groups in organic interlayers, which enhance membrane negative charge and facilitate the retention of negatively charged sodium sulfate.

5. Concluding Remarks and Future Perspectives

The incorporation of interlayers onto the substrate during the preparation of NF membranes has been demonstrated to effectively enhance their performance. Various materials, including NPs, organic polymers, 1D nanomaterials, and 2D nanomaterials, have been investigated as interlayers for TFC NF membrane preparation (Table 1 and Table 2). TFC NF membranes with high salt rejection and permeability have been developed using all types of interlayer materials. Among them, 1D nanomaterials exhibit better flux improvement, while organic and 2D nanomaterials demonstrate superior salt rejection ability. However, TFC NF membranes utilizing interlayers are still in the early stages of development. To advance the development of high-performance TFC NF membranes using interlayers, it is necessary to address several issues.
  • Interlayer materials. Considering that 1D nanomaterials are most effective in improving membrane flux, and organic polymers and 2D nanomaterials are good at improving salt rejection ability, composite materials such as organic/1D nanomaterials and 2D/1D nanomaterials may be candidate materials for preparing high-performance NF membranes. Some researchers have introduced PDA/CNT as an interlayer for the preparation of NF membranes [54,55,56]. In addition to enhancing the selectivity of the NF membrane, the function of PDA can also serve as an adhesive to encapsulate CNTs, thereby improving the stability of the TFC NF membrane. Some other researchers have directly used organic 1D nanomaterials (such as Polyaniline nanofibers [60] and microporous organic nanotubes [63]) as interlayers to prepare NF membranes with not only extremely high flux (>40 L m2− h−1 bar−1) but also high salt rejection ability (rejection of Na2SO4 > 98%) (see Table 2). Organic 1D nanomaterials have more hydrophilic functional groups and better chemical stability than inorganic 1D nanomaterials (such as CNTs), combining the advantages of both inorganic 1D nanomaterials and organic polymers. Moreover, to date, there have been no reports on 2D/1D nanomaterials used as interlayer materials for preparing NF membranes, although 2D/1D nanomaterials (such as MXene/CNTs [89]) have been reported to be used for preparing high-performance 2D membranes. Given the effectiveness of these materials as interlayers, it is necessary to further explore the possibility of using other composite materials (such as organic polymer/1D nanomaterials, 2D/1D nanomaterials) and organic 1D nanomaterials as interlayers for preparing high-performance NF membranes. The selection of interlayer materials must also consider factors such as compatibility with the substrate, preparation difficulty, stability under operating conditions, and cost-effectiveness.
  • Current studies in membrane technology have largely focused on enhancing permeability, but there is also a pressing need for membranes that exhibit high selectivity towards specific solutes. Interlayers have shown promise in addressing this need by allowing for the customization of membrane properties to selectively adsorb or repel certain solutes, thereby enhancing selectivity. Notably, Zhu et al. [38] introduced positively charged quaternized cross-linked microgels (PNI6) as an interlayer to improve Mg2+ removal, demonstrating the ability of interlayers to significantly impact the selectivity of PA membranes. An exciting avenue for future research is exploring how the unique chemical properties of interlayer materials can be harnessed to enhance selectivity towards specific pollutants [90,91,92].
  • Another important aspect of developing interlayer-based TFC NF membranes is the need for scalable and cost-effective manufacturing methods. While many promising results have been reported in the literature, most of these methods are still confined to the laboratory scale and may not be suitable for large-scale production. Therefore, further research is necessary to develop scalable methods that can be seamlessly integrated into existing membrane manufacturing processes.
  • Moreover, it is crucial to conduct comprehensive investigations into the long-term stability and durability of interlayer-based TFC NF membranes under diverse operating conditions. Although several studies have reported positive outcomes in terms of membrane performance, few have explored the impact of contamination, chemical degradation, and other factors on membrane performance over extended periods of use. Hence, more extensive research is necessary to evaluate the effects of these factors on membrane performance over time.
  • Current studies on the preparation of nanofiltration membranes with an interlayer primarily focus on achieving a balance between permeability and selectivity, and there is limited research on the interlayer’s impact on anti-pollution properties. However, the impact of the interlayer on anti-fouling performance is essential in the development of nanofiltration membranes. Moving forward, we expect that further research in this area will lead to the development of novel interlayer materials and strategies that can improve both permeability/selectivity and pollution resistance simultaneously.
  • During the preparation of TFC NF membranes, controlling the dispersion of nanomaterials is crucial to avoid aggregation and ensure optimal performance. Existing literature has used various methods such as surface modification (carboxylation treatment of MWCNTs [16]), dispersion in solutions such as PDA [54,56], polyvinyl alcohol sodium [69], dodecyl benzene sulfonate [51], sodium dodecylbenzene sulfonate [56], Tris-HCl buffer [47], and ultrasound treatment [21,47,51,52,53,54,56,69,72,75,87] to prevent the agglomeration of nanomaterials. While there are many methods available to avoid the agglomeration of nanomaterials, there is always room for improvement and the development of new methods. This is because the properties and behavior of nanomaterials can be complex and difficult to predict, and different applications may require different strategies for preventing agglomeration. Additionally, as new types of nanomaterials are developed and used in various applications, new methods for avoiding agglomeration may need to be developed as well. Therefore, continued research and development in this area is necessary to optimize the performance of nanomaterials in various applications.
  • In conclusion, while there are significant challenges in the application of interlayer materials in the preparation of TFC PA NF membranes, this field holds enormous potential for enhancing membrane performance and extending its scope of applications. Through sustained research and development in this area, we may witness substantial progress in membrane technology in the forthcoming years.

Author Contributions

Conceptual design, L.Z.; methodology, L.Z.; formal analysis, L.Z.; investigation, M.L.; data curation, N.G.; writing—preparation of draft, M.L.; writing—review and revision, M.L.; visualization, N.G.; acquisition of funding, L.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the Science Research Project at the Universities of Anhui Province for Distinguished Young Scholars (2022AH020070), the Major University Science Research Project of Anhui Province (KJ2021ZD0132), the top-notch scholarship program at the Universities of Anhui Province (gxbjZD2022071).

Institutional Review Board Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Dai, R.; Li, J.; Wang, Z. Constructing interlayer to tailor structure and performance of thin-film composite polyamide membranes: A review. Colloid Interface Sci. 2020, 282, 102204. [Google Scholar] [CrossRef] [PubMed]
  2. Park, H.B.; Kamcev, J.; Robeson, L.M.; Elimelech, M.; Freeman, B.D. Maximizing the right stuff: The trade-off between membrane permeability and selectivity. Science 2017, 356, eaab0530. [Google Scholar] [CrossRef] [PubMed]
  3. Yang, Z.; Guo, H.; Tang, C.Y. The upper bound of thin-film composite (TFC) polyamide membranes for desalination. J. Membr. Sci. 2019, 590, 117297. [Google Scholar] [CrossRef]
  4. Lau, W.J.; Gray, S.; Matsuura, T.; Emadzadeh, D.; Chen, J.P.; Ismail, A.F. A review on polyamide thin film nanocomposite (TFN) membranes: History, applications, challenges and approaches. Water Res. 2015, 80, 306–324. [Google Scholar] [CrossRef]
  5. Lau, W.J.; Ismail, A.F.; Misdan, N.; Kassim, M.A. A recent progress in thin film composite membrane: A review. Desalination 2012, 287, 190–199. [Google Scholar] [CrossRef]
  6. Choi, W.; Gu, J.-E.; Park, S.-H.; Kim, S.; Bang, J.; Baek, K.-Y.; Park, B.; Lee, J.S.; Chan, E.P.; Lee, J.-H. Tailor-Made Polyamide Membranes for Water Desalination. ACS Nano 2015, 9, 345–355. [Google Scholar] [CrossRef]
  7. Freger, V. Nanoscale heterogeneity of polyamide membranes formed by interfacial polymerization. Langmuir 2003, 19, 4791–4797. [Google Scholar] [CrossRef]
  8. Freger, V.; Srebnik, S. Mathematical model of charge and density distributions in interfacial polymerization of thin films. J. Appl. Polym. Sci. 2003, 88, 1162–1169. [Google Scholar] [CrossRef]
  9. Mohammad, A.W.; Teow, Y.H.; Ang, W.L.; Chung, Y.T.; Oatley-Radcliffe, D.L.; Hilal, N. Nanofiltration membranes review: Recent advances and future prospects. Desalination 2015, 356, 226–254. [Google Scholar] [CrossRef]
  10. Nowbahar, A.; Mansard, V.; Mecca, J.M.; Paul, M.; Arrowood, T.; Squires, T.M. Measuring interfacial polymerization kinetics using microfluidic interferometry. J. Am. Chem. Soc. 2018, 140, 3173–3176. [Google Scholar] [CrossRef]
  11. Liang, Y.; Li, C.; Li, S.; Su, B.; Hu, M.Z.; Gao, X.; Gao, C. Graphene quantum dots (GQDs)-polyethyleneimine as interlayer for the fabrication of high performance organic solvent nanofiltration (OSN) membranes. Chem. Eng. J. 2020, 380, 122462. [Google Scholar] [CrossRef]
  12. Geise, G.M.; Paul, D.R.; Freeman, B.D. Fundamental water and salt transport properties of polymeric materials. Prog. Polym. Sci. 2014, 39, 1–42. [Google Scholar] [CrossRef]
  13. Liu, G.; Jin, W.; Xu, N. Graphene-based membranes. Chem. Soc. Rev. 2015, 44, 5016–5030. [Google Scholar] [CrossRef] [PubMed]
  14. Karan, S.; Jiang, Z.; Livingston, A.G. Sub-10 nm polyamide nanofilms with ultrafast solvent transport for molecular separation. Science 2015, 348, 1347–1351. [Google Scholar] [CrossRef]
  15. Jimenez-Solomon, M.F.; Song, Q.; Jelfs, K.E.; Munoz-Ibanez, M.; Livingston, A.G. Polymer nanofilms with enhanced microporosity by interfacial polymerization. Nat. Mater. 2016, 15, 760–768. [Google Scholar] [CrossRef]
  16. Wu, M.-B.; Lv, Y.; Yang, H.-C.; Liu, L.-F.; Zhang, X.; Xu, Z.-K. Thin film composite membranes combining carbon nanotube intermediate layer and microfiltration support for high nanofiltration performances. J. Membr. Sci. 2016, 515, 238–244. [Google Scholar] [CrossRef]
  17. Zhu, J.; Hou, J.; Zhang, R.; Yuan, S.; Li, J.; Tian, M.; Wang, P.; Zhang, Y.; Volodin, A.; Van der Bruggen, B. Rapid water transport through controllable, ultrathin polyamide nanofilms for high-performance nanofiltration. J. Mater. Chem. A 2018, 6, 15701–15709. [Google Scholar] [CrossRef]
  18. Lau, W.-J.; Lai, G.-S.; Li, J.; Gray, S.; Hu, Y.; Misdan, N.; Goh, P.-S.; Matsuura, T.; Azelee, I.W.; Ismail, A.F. Development of microporous substrates of polyamide thin film composite membranes for pressure-driven and osmotically-driven membrane processes: A review. J. Ind. Eng. Chem. 2019, 77, 25–59. [Google Scholar] [CrossRef]
  19. Yang, X.; Du, Y.; Zhang, X.; He, A.; Xu, Z.K. Nanofiltration membrane with a mussel-inspired interlayer for improved permeation performance. Langmuir 2017, 33, 2318–2324. [Google Scholar] [CrossRef]
  20. Yang, Z.; Wang, F.; Guo, H.; Peng, L.E.; Ma, X.H.; Song, X.X.; Wang, Z.; Tang, C.Y. Mechanistic insights into the role of polydopamine interlayer toward improved separation performance of polyamide nanofiltration membranes. Environ. Sci. Technol. 2020, 54, 11611–11621. [Google Scholar] [CrossRef]
  21. Long, L.; Wu, C.; Yang, Z.; Tang, C.Y. Carbon nanotube interlayer enhances water permeance and antifouling performance of nanofiltration membranes: Mechanisms and experimental evidence. Environ. Sci. Technol. 2022, 56, 2656–2664. [Google Scholar] [CrossRef] [PubMed]
  22. Yang, Z.; Sun, P.F.; Li, X.; Gan, B.; Wang, L.; Song, X.; Park, H.D.; Tang, C.Y. A Critical Review on Thin-Film Nanocomposite Membranes with Interlayered Structure: Mechanisms, Recent Developments, and Environmental Applications. Environ. Sci. Technol. 2020, 54, 15563–15583. [Google Scholar] [CrossRef] [PubMed]
  23. Kausar, A. Polymer coating technology for high performance applications: Fundamentals and advances. J. Macromol. Sci. A 2018, 55, 440–448. [Google Scholar] [CrossRef]
  24. Ulbricht, M. Design and synthesis of organic polymers for molecular separation membranes. Curr. Opin. Chem. Eng. 2020, 28, 60–65. [Google Scholar] [CrossRef]
  25. Zhai, Z.; Jiang, C.; Zhao, N.; Dong, W.; Lan, H.; Wang, M.; Niu, Q.J. Fabrication of advanced nanofiltration membranes with nanostrand hybrid morphology mediated by ultrafast Noria–polyethyleneimine codeposition. J. Mater. Chem. A 2018, 6, 21207–21215. [Google Scholar] [CrossRef]
  26. Qiu, W.-Z.; Yang, H.-C.; Wan, L.-S.; Xu, Z.-K. Co-deposition of catechol/polyethyleneimine on porous membranes for efficient decolorization of dye water. J. Mater. Chem. A 2015, 3, 14438–14444. [Google Scholar] [CrossRef]
  27. Zhu, X.; Cheng, X.; Luo, X.; Liu, Y.; Xu, D.; Tang, X.; Gan, Z.; Yang, L.; Li, G.; Liang, H. Ultrathin thin-Film composite polyamide membranes constructed on hydrophilic poly(vinyl alcohol) decorated support toward enhanced nanofiltration performance. Environ. Sci. Technol. 2020, 54, 6365–6374. [Google Scholar] [CrossRef]
  28. Singla, R.K.; Dubey, A.K.; Garg, A.; Sharma, R.K.; Fiorino, M.; Ameen, S.M.; Haddad, M.A.; Al-Hiary, M. Natural Polyphenols: Chemical Classification, Definition of Classes, Subcategories, and Structures. J. AOAC Int. 2019, 102, 1397–1400. [Google Scholar] [CrossRef]
  29. Yang, H.C.; Waldman, R.Z.; Wu, M.B.; Hou, J.; Chen, L.; Darling, S.B.; Xu, Z.K. Dopamine: Just the Right Medicine for Membranes. Adv. Funct. Mater. 2018, 28, 1705327. [Google Scholar] [CrossRef]
  30. Zhang, X.; Lv, Y.; Yang, H.-C.; Du, Y.; Xu, Z.-K. Polyphenol coating as an interlayer for thin-film composite membranes with enhanced nanofiltration performance. ACS Appl. Mater Inter. 2016, 8, 32512–32519. [Google Scholar] [CrossRef]
  31. Zhao, S.; Li, L.; Wang, M.; Tao, L.; Hou, Y.; Niu, Q.J. Rapid in-situ covalent crosslinking to construct a novel azo-based interlayer for high-performance nanofiltration membrane. Sep. Purif. Technol. 2021, 258, 118029. [Google Scholar] [CrossRef]
  32. Yang, Z.; Zhou, Z.-w.; Guo, H.; Yao, Z.; Ma, X.-h.; Song, X.; Feng, S.-P.; Tang, C.Y. Tannic acid/Fe3+ nanoscaffold for interfacial polymerization: Toward enhanced nanofiltration performance. Environ. Sci. Technol. 2018, 52, 9341–9349. [Google Scholar] [CrossRef] [PubMed]
  33. Chen, K.; Zhao, S.; Lan, H.; Xie, T.; Wang, H.; Chen, Y.; Li, P.; Sun, H.; Niu, Q.J.; Yang, C. Dual-electric layer nanofiltration membranes based on polyphenol/PEI interlayer for highly efficient Mg2+/Li+ separation. J. Membr. Sci. 2022, 660, 120860. [Google Scholar] [CrossRef]
  34. Sun, H.; Liu, J.; Luo, X.; Chen, Y.; Jiang, C.; Zhai, Z.; Niu, Q.J. Fabrication of thin-film composite polyamide nanofiltration membrane based on polyphenol intermediate layer with enhanced desalination performance. Desalination 2020, 488, 114525. [Google Scholar] [CrossRef]
  35. Tian, B.; Hu, P.; Zhao, S.; Wang, M.; Hou, Y.; Niu, Q.J.; Li, P. Nanofiltration membrane combining environmental-friendly polycarboxylic interlayer prepared from catechol for enhanced desalination performance. Desalination 2021, 512, 115118. [Google Scholar] [CrossRef]
  36. Hu, P.; Tian, B.; Xu, Z.; Niu, Q.J. Fabrication of high performance nanofiltration membrane on a coordination-driven assembled interlayer for water purification. Sep. Purif. Technol. 2020, 235, 116192. [Google Scholar] [CrossRef]
  37. Deng, M.; Pei, T.; Ge, P.; Zhu, A.; Zhang, Q.; Liu, Q. Ultrathin sulfonated mesoporous interlayer facilitates to prepare highly-permeable polyamide nanofiltration membranes. J. Membr. Sci. 2022, 652, 120507. [Google Scholar] [CrossRef]
  38. Zhu, S.; Dong, S.; Fan, W.; Nie, J.; Zhu, L.; Du, B. Preparation of high-performance nanofiltration membranes with quaternized cross-linked microgels as intermediate layer. Desalination 2023, 549, 116310. [Google Scholar] [CrossRef]
  39. Song, Q.; Lin, Y.; Zhou, S.; Istirokhatun, T.; Wang, Z.; Shen, Q.; Mai, Z.; Guan, K.; Matsuyama, H. Highly permeable nanofilms with asymmetric multilayered structure engineered via amine-decorated interlayered interfacial polymerization. J. Membr. Sci. 2023, 670, 121377. [Google Scholar] [CrossRef]
  40. Song, Q.; Lin, Y.; Ueda, T.; Shen, Q.; Lee, K.-R.; Yoshioka, T.; Matsuyama, H. A zwitterionic copolymer-interlayered ultrathin nanofilm with ridge-shaped structure for ultrapermeable nanofiltration. J. Membr. Sci. 2022, 657, 120679. [Google Scholar] [CrossRef]
  41. Liu, M.; Chen, W.; Fu, J.; Wang, A.; Ding, M.; Zhang, L.; Han, L.; Gao, L. Hyaluronic acid-modified nanofiltration membrane for ultrahigh water permeance and efficient rejection of PFASs. Process Saf. Environ. Prot. 2022, 166, 214–221. [Google Scholar] [CrossRef]
  42. Wang, X.-L.; Xue, Y.-X.; Dong, S.-Q.; Wang, Q.; Yu, J.-T.; Wang, H.-C.; Zhang, H.; Wang, W.; Wei, J.-F. Poly(caffeic acid) as interlayer to enhance nanofiltration performance of polyamide composite membrane. Desalination 2023, 545, 116168. [Google Scholar] [CrossRef]
  43. Lan, H.; Li, P.; Wang, H.; Wang, M.; Jiang, C.; Hou, Y.; Li, P.; Jason Niu, Q. Construction of a gelatin scaffold with water channels for preparing a high performance nanofiltration membrane. Sep. Purif. Technol. 2021, 264, 118391. [Google Scholar] [CrossRef]
  44. Liu, Z.; An, Z.; Mi, Z.; Wang, Z.; Zhu, Q.; Zhang, D.; Wang, J.; Liu, J.; Zhang, J. Thin-film composite nanofiltration membranes with poly (amidoxime) as organic interlayer for effective desalination. J. Environ. Chem. Eng. 2022, 10, 107015. [Google Scholar] [CrossRef]
  45. Chen, Y.; Sun, H.; Tang, S.; Feng, H.; Zhang, H.; Chen, K.; Li, P.; Niu, Q.J. Nanofiltration membranes with enhanced performance by constructing an interlayer integrated with dextran nanoparticles and polyethyleneimine coating. J. Membr. Sci. 2022, 654, 120537. [Google Scholar] [CrossRef]
  46. Song, Q.; Lin, Y.; Ueda, T.; Istirokhatun, T.; Shen, Q.; Guan, K.; Yoshioka, T.; Matsuyama, H. Mechanism insights into the role of the support mineralization layer toward ultrathin polyamide nanofilms for ultrafast molecular separation. J. Mater. Chem. A 2021, 9, 26159–26171. [Google Scholar] [CrossRef]
  47. Wang, Y.; Wang, T.; Li, S.; Zhao, Z.; Zheng, X.; Zhang, L.; Zhao, Z. Novel Poly(piperazinamide)/poly(m-phenylene isophthalamide) composite nanofiltration membrane with polydopamine coated silica as an interlayer for the splendid performance. Sep. Purif. Technol. 2022, 285, 120390. [Google Scholar] [CrossRef]
  48. Han, S.; Mai, Z.; Wang, Z.; Zhang, X.; Zhu, J.; Shen, J.; Wang, J.; Wang, Y.; Zhang, Y. Covalent organic framework-mediated thin-film composite polyamide membranes toward precise ion sieving. ACS Appl. Mater Inter. 2022, 14, 3427–3436. [Google Scholar] [CrossRef]
  49. Zhao, B.; Guo, Z.; Wang, H.; Wang, L.; Qian, Y.; Long, X.; Ma, C.; Zhang, Z.; Li, J.; Zhang, H. Enhanced water permeance of a polyamide thin-film composite nanofiltration membrane with a metal-organic framework interlayer. J. Membr. Sci. 2021, 625, 119154. [Google Scholar] [CrossRef]
  50. Irigoyen, J.; Laakso, T.; Politakos, N.; Dahne, L.; Pihlajamaki, A.; Manttari, M.; Enrique Moya, S. Design and Performance Evaluation of Hybrid Nanofiltration Membranes Based on Multiwalled Carbon Nanotubes and Polyelectrolyte Multilayers for Larger Ion Rejection and Separation. Macromol. Chem. Phys. 2016, 217, 804–811. [Google Scholar] [CrossRef]
  51. Gao, S.; Zhu, Y.; Gong, Y.; Wang, Z.; Fang, W.; Jin, J. Ultrathin polyamide nanofiltration membrane fabricated on brush-painted single-walled carbon nanotube network support for ion sieving. ACS Nano 2019, 13, 5278–5290. [Google Scholar] [CrossRef]
  52. Park, M.J.; Wang, C.; Seo, D.H.; Gonzales, R.R.; Matsuyama, H.; Shon, H.K. Inkjet printed single walled carbon nanotube as an interlayer for high performance thin film composite nanofiltration membrane. J. Membr. Sci. 2021, 620, 118901. [Google Scholar] [CrossRef]
  53. Wang, J.-J.; Yang, H.-C.; Wu, M.-B.; Zhang, X.; Xu, Z.-K. Nanofiltration membranes with cellulose nanocrystals as an interlayer for unprecedented performance. J. Mater. Chem. A 2017, 5, 16289–16295. [Google Scholar] [CrossRef]
  54. Zhu, Y.; Xie, W.; Gao, S.; Zhang, F.; Zhang, W.; Liu, Z.; Jin, J. Single-walled carbon nanotube film supported nanofiltration membrane with a nearly 10 nm thick polyamide selective layer for high-flux and high-rejection desalination. Small 2016, 12, 5034–5041. [Google Scholar] [CrossRef] [PubMed]
  55. Wang, Z.; Wang, Z.; Lin, S.; Jin, H.; Gao, S.; Zhu, Y.; Jin, J. Nanoparticle-templated nanofiltration membranes for ultrahigh performance desalination. Nat.Commun. 2018, 9, 2004. [Google Scholar] [CrossRef] [PubMed]
  56. Gong, G.; Wang, P.; Zhou, Z.; Hu, Y. New insights into the role of an interlayer for the fabrication of highly selective and permeable thin-film composite nanofiltration membrane. ACS Appl. Mater. Inter. 2019, 11, 7349–7356. [Google Scholar] [CrossRef] [PubMed]
  57. Zhao, X.; Liu, R. Recent progress and perspectives on the toxicity of carbon nanotubes at organism, organ, cell, and biomacromolecule levels. Environ. Int. 2012, 40, 244–255. [Google Scholar] [CrossRef] [PubMed]
  58. Thompson, J.; Bannigan, J. Cadmium: Toxic effects on the reproductive system and the embryo. Reprod. Toxicol. 2008, 25, 304–315. [Google Scholar] [CrossRef]
  59. Wang, Z.-Y.; Xie, F.; Ding, H.-Z.; Huang, W.; Ma, X.-H.; Xu, Z.-L. Effects of locations of cellulose nanofibers in membrane on the performance of positively charged membranes. J. Membr. Sci. 2022, 652, 120464. [Google Scholar] [CrossRef]
  60. Ji, C.; Lin, C.-W.; Zhang, S.; Guo, Y.; Yang, Z.; Hu, W.; Xue, S.; Niu, Q.J.; Kaner, R.B. Ultrapermeable nanofiltration membranes with tunable selectivity fabricated with polyaniline nanofibers. J. Mater. Chem. A 2022, 10, 4392–4401. [Google Scholar] [CrossRef]
  61. Guo, Y.; Ji, C.; Ye, Y.; Chen, Y.; Yang, Z.; Xue, S.; Niu, Q.J. High performance nanofiltration membrane using self-doping sulfonated polyaniline. J. Membr. Sci. 2022, 652, 120441. [Google Scholar] [CrossRef]
  62. Guo, Y.; Wei, S.; Chen, Y.; Ye, H.; Xue, S.; Niu, Q.J. Sulfonated polyaniline interlayer with controllable doping conditions for high-performance nanofiltration. J. Membr. Sci. 2023, 672, 121478. [Google Scholar] [CrossRef]
  63. Han, S.; Zhu, J.; Uliana, A.A.; Li, D.; Zhang, Y.; Zhang, L.; Wang, Y.; He, T.; Elimelech, M. Microporous organic nanotube assisted design of high performance nanofiltration membranes. Nat. Commun. 2022, 13, 7954. [Google Scholar] [CrossRef] [PubMed]
  64. Xue, S.-M.; Ji, C.-H.; Xu, Z.-L.; Tang, Y.-J.; Li, R.-H. Chlorine resistant TFN nanofiltration membrane incorporated with octadecylamine-grafted GO and fluorine-containing monomer. J. Membr. Sci. 2018, 545, 185–195. [Google Scholar] [CrossRef]
  65. Medhekar, N.V.; Ramasubramaniam, A.; Ruoff, R.S.; Shenoy, V.B. Hydrogen Bond Networks in Graphene Oxide Composite Paper: Structure and Mechanical Properties. ACS Nano 2010, 4, 2300–2306. [Google Scholar] [CrossRef]
  66. Lim, M.-Y.; Choi, Y.-S.; Kim, J.; Kim, K.; Shin, H.; Kim, J.-J.; Shin, D.M.; Lee, J.-C. Cross-linked graphene oxide membrane having high ion selectivity and antibacterial activity prepared using tannic acid-functionalized graphene oxide and polyethyleneimine. J. Membr. Sci. 2017, 521, 1–9. [Google Scholar] [CrossRef]
  67. Wang, C.; Li, Z.; Chen, J.; Yin, Y.; Wu, H. Structurally stable graphene oxide-based nanofiltration membranes with bioadhesive polydopamine coating. Appl. Surf. Sci. 2018, 427, 1092–1098. [Google Scholar] [CrossRef]
  68. Aburabie, J.; Peinemann, K.-V. Crosslinked poly(ether block amide) composite membranes for organic solvent nanofiltration applications. J. Membr. Sci. 2017, 523, 264–272. [Google Scholar] [CrossRef]
  69. Zhang, J.; Li, S.; Ren, D.; Li, H.; Lv, X.; Han, L.; Su, B. Fabrication of ultra-smooth thin-film composite nanofiltration membrane with enhanced selectivity and permeability on interlayer of hybrid polyvinyl alcohol and graphene oxide. Sep. Purif. Technol. 2021, 268, 118649. [Google Scholar] [CrossRef]
  70. Wang, S.; Mahalingam, D.; Sutisna, B.; Nunes, S.P. 2D-dual-spacing channel membranes for high performance organic solvent nanofiltration. J. Mater. Chem. A 2019, 7, 11673–11682. [Google Scholar] [CrossRef]
  71. Ding, L.; Li, L.; Liu, Y.; Wu, Y.; Lu, Z.; Deng, J.; Wei, Y.; Caro, J.; Wang, H. Effective ion sieving with Ti3C2Tx MXene membranes for production of drinking water from seawater. Nat. Sustain. 2020, 3, 296–302. [Google Scholar] [CrossRef]
  72. Xu, D.; Zhu, X.; Luo, X.; Guo, Y.; Liu, Y.; Yang, L.; Tang, X.; Li, G.; Liang, H. MXene Nanosheet templated nanofiltration membranes toward ultrahigh water transport. Environ. Sci. Technol. 2021, 55, 1270–1278. [Google Scholar] [CrossRef] [PubMed]
  73. Yu, L.; Ling, R.; Chen, J.P.; Reinhard, M. Quantitative assessment of the iron-catalyzed degradation of a polyamide nanofiltration membrane by hydrogen peroxide. J. Membr. Sci. 2019, 588, 117154. [Google Scholar] [CrossRef]
  74. Ling, R.; Yu, L.; Thi Phuong Thuy, P.; Shao, J.; Chen, J.P.; Reinhard, M. Catalytic effect of iron on the tolerance of thin-film composite polyamide reverse osmosis membranes to hydrogen peroxide. J. Membr. Sci. 2018, 548, 91–98. [Google Scholar] [CrossRef]
  75. Zhu, X.; Zhang, X.; Li, J.; Luo, X.; Xu, D.; Wu, D.; Wang, W.; Cheng, X.; Li, G.; Liang, H. Crumple-textured polyamide membranes via MXene nanosheet-regulated interfacial polymerization for enhanced nanofiltration performance. J. Membr. Sci. 2021, 635, 119536. [Google Scholar] [CrossRef]
  76. Cao, S.; Deshmukh, A.; Wang, L.; Han, Q.; Shu, Y.; Ng, H.Y.; Wang, Z.; Lienhard, J.H. Enhancing the permselectivity of thin-film composite membranes interlayered with MoS2 nanosheets via precise thickness control. Environ. Sci. Technol. 2022, 56, 8807–8818. [Google Scholar] [CrossRef] [PubMed]
  77. Aydiner, C. A model-based analysis of water transport dynamics and fouling behaviors of osmotic membrane. Chem. Eng. J. 2015, 266, 289–298. [Google Scholar] [CrossRef]
  78. Wang, A.; Xu, H.; Fu, J.; Lin, T.; Ma, J.; Ding, M.; Gao, L. Enhanced high-salinity brines treatment using polyamide nanofiltration membrane with tunable interlayered MXene channel. Sci. Total Environ. 2022, 856, 158434. [Google Scholar] [CrossRef]
  79. Fu, J.; Xu, H.; Lin, T.; Wang, A.; Wang, A.; Yao, C.; Chen, W.; Ding, M.; Geng, C.; Gao, L. Tailoring the crumpled structures of a polyamide membrane with a heterostructural MXene-TiO2 interlayer for high water permeability. Desalination 2023, 549, 116352. [Google Scholar] [CrossRef]
  80. Wang, F.; Yang, C.; Duan, M.; Tang, Y.; Zhu, J. TiO2 nanoparticle modified organ-like Ti3C2 MXene nanocomposite encapsulating hemoglobin for a mediator-free biosensor with excellent performances. Biosens. Bioelectron. 2015, 74, 1022–1028. [Google Scholar] [CrossRef]
  81. Gao, W.; Li, X.; Luo, S.; Luo, Z.; Zhang, X.; Huang, R.; Luo, M. In situ modification of cobalt on MXene/TiO2 as composite photocatalyst for efficient nitrogen fixation. J. Colloid Interf. Sci. 2021, 585, 20–29. [Google Scholar] [CrossRef] [PubMed]
  82. Jin, Y.; Hu, Y.; Zhang, W. Tessellated multiporous two-dimensional covalent organic frameworks. Nat. Rev. Chem. 2017, 1, 0056. [Google Scholar] [CrossRef]
  83. Biswal, B.P.; Chandra, S.; Kandambeth, S.; Lukose, B.; Heine, T.; Banerjeet, R. Mechanochemical Synthesis of Chemically Stable Isoreticular Covalent Organic Frameworks. J. Am. Chem. Soc. 2013, 135, 5328–5331. [Google Scholar] [CrossRef] [PubMed]
  84. Wu, M.; Yuan, J.; Wu, H.; Su, Y.; Yang, H.; You, X.; Zhang, R.; He, X.; Khan, N.A.; Kasher, R.; et al. Ultrathin nanofiltration membrane with polydopamine-covalent organic framework interlayer for enhanced permeability and structural stability. J. Membr. Sci. 2019, 576, 131–141. [Google Scholar] [CrossRef]
  85. Yuan, J.; Wu, M.; Wu, H.; Liu, Y.; You, X.; Zhang, R.; Su, Y.; Yang, H.; Shen, J.; Jiang, Z. Covalent organic framework-modulated interfacial polymerization for ultrathin desalination membranes. J. Mater. Chem. A 2019, 7, 25641–25649. [Google Scholar] [CrossRef]
  86. Cheng, P.; Liu, Y.; Wang, X.; Fan, K.; Li, P.; Xia, S. Regulating interfacial polymerization via constructed 2D metal-organic framework interlayers for fabricating nanofiltration membranes with enhanced performance. Desalination 2022, 544, 116134. [Google Scholar] [CrossRef]
  87. Kang, X.; Liu, X.; Liu, J.; Wen, Y.; Qi, J.; Li, X. Spin-assisted interfacial polymerization strategy for graphene oxide-polyamide composite nanofiltration membrane with high performance. Appl. Surf. Sci. 2020, 508, 145198. [Google Scholar] [CrossRef]
  88. Xue, S.; Lin, C.W.; Ji, C.; Guo, Y.; Liu, L.; Yang, Z.; Zhao, S.; Cai, X.; Niu, Q.J.; Kaner, R.B. Thin-film composite membranes with a hybrid dimensional titania interlayer for ultrapermeable nanofiltration. Nano Lett. 2022, 22, 1039–1046. [Google Scholar] [CrossRef]
  89. Ding, M.; Xu, H.; Chen, W.; Kong, Q.; Lin, T.; Tao, H.; Zhang, K.; Liu, Q.; Zhang, K.; Xie, Z. Construction of a hierarchical carbon nanotube/MXene membrane with distinct fusiform channels for efficient molecular separation. J. Mater. Chem. A 2020, 8, 22666–22673. [Google Scholar] [CrossRef]
  90. Guo, H.; Deng, Y.; Tao, Z.; Yao, Z.; Wang, J.; Lin, C.; Zhang, T.; Zhu, B.; Tang, C.Y. Does Hydrophilic Polydopamine Coating Enhance Membrane Rejection of Hydrophobic Endocrine-Disrupting Compounds? Environ. Sci. Technol. Lett. 2016, 3, 332–338. [Google Scholar] [CrossRef]
  91. Guo, H.; Yao, Z.; Yang, Z.; Ma, X.; Wang, J.; Tang, C.Y. A One-Step Rapid Assembly of Thin Film Coating Using Green Coordination Complexes for Enhanced Removal of Trace Organic Contaminants by Membranes. Environ. Sci. Technol. 2017, 51, 12638–12643. [Google Scholar] [CrossRef] [PubMed]
  92. Guo, H.; Deng, Y.; Yao, Z.; Yang, Z.; Wang, J.; Lin, C.; Zhang, T.; Zhu, B.; Tang, C.Y. A highly selective surface coating for enhanced membrane rejection of endocrine disrupting compounds: Mechanistic insights and implications. Water Res. 2017, 121, 197–203. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Schematic diagram of (a) conventional substrate and (b) P[MPC-co-AEMA] inter-mediated IP with the underlying mechanism of (c) enrichment effect and retardation effect. Reprinted with permission from ref. [40]. Copyright 2022 Elsevier.
Figure 1. Schematic diagram of (a) conventional substrate and (b) P[MPC-co-AEMA] inter-mediated IP with the underlying mechanism of (c) enrichment effect and retardation effect. Reprinted with permission from ref. [40]. Copyright 2022 Elsevier.
Membranes 13 00497 g001
Figure 2. Process flowchart for the preparation of TFC NF membrane with an interlayer. Reprinted with permission from ref. [45]. Copyright 2022 Elsevier.
Figure 2. Process flowchart for the preparation of TFC NF membrane with an interlayer. Reprinted with permission from ref. [45]. Copyright 2022 Elsevier.
Membranes 13 00497 g002
Figure 3. Schematic diagram of (a) silicification inter-mediated IP with the underlying mechanism of (b) amine monomer adsorption enrichment and diffusion restriction toward the organic phase for (c) developing ultra-thin, highly crosslinked PA nanofiltration membrane. Reprinted with permission from ref. [46]. Copyright 2022 Royal Society of Chemistry.
Figure 3. Schematic diagram of (a) silicification inter-mediated IP with the underlying mechanism of (b) amine monomer adsorption enrichment and diffusion restriction toward the organic phase for (c) developing ultra-thin, highly crosslinked PA nanofiltration membrane. Reprinted with permission from ref. [46]. Copyright 2022 Royal Society of Chemistry.
Membranes 13 00497 g003
Figure 4. Schematic diagram of (a) MON inter-mediated IP with the underlying mechanism of (b) hydrogen bonding and electrostatic interactions. Reprinted with permission from ref. [63]. Copyright 2022 Springer.
Figure 4. Schematic diagram of (a) MON inter-mediated IP with the underlying mechanism of (b) hydrogen bonding and electrostatic interactions. Reprinted with permission from ref. [63]. Copyright 2022 Springer.
Membranes 13 00497 g004
Figure 5. Schematic diagram of MXene inter-mediated IP. Reprinted with permission from ref. [75]. Copyright 2021 Elsevier.
Figure 5. Schematic diagram of MXene inter-mediated IP. Reprinted with permission from ref. [75]. Copyright 2021 Elsevier.
Membranes 13 00497 g005
Figure 6. Statistical analysis of (a) water permeability and (b) Na2SO4 rejection of TFC0 and TFCi NF membranes [27,35,40,41,46,52,60,63,75,86]. Statistical analysis of (c) water permeability and (d) Na2SO4 rejection based on NPs [46,47,48,49] 1D [51,52,53,54,55,56,60,61,63], 2D nanomaterials [69,72,75,76,84,85,86,87], and Organic interlayers [25,27,31,34,35,36,38,39,40,41,42,43,44,45]. This is a rough comparison as the substrates used in these publications are not similar, and the substrate has an impact on the formation of PA membranes by IP. Moreover, the IP conditions are different, which also affects the separation performance of the membranes.
Figure 6. Statistical analysis of (a) water permeability and (b) Na2SO4 rejection of TFC0 and TFCi NF membranes [27,35,40,41,46,52,60,63,75,86]. Statistical analysis of (c) water permeability and (d) Na2SO4 rejection based on NPs [46,47,48,49] 1D [51,52,53,54,55,56,60,61,63], 2D nanomaterials [69,72,75,76,84,85,86,87], and Organic interlayers [25,27,31,34,35,36,38,39,40,41,42,43,44,45]. This is a rough comparison as the substrates used in these publications are not similar, and the substrate has an impact on the formation of PA membranes by IP. Moreover, the IP conditions are different, which also affects the separation performance of the membranes.
Membranes 13 00497 g006
Table 1. Structure and performance of TFC NF membranes with organic interlayer.
Table 1. Structure and performance of TFC NF membranes with organic interlayer.
CategoryOrganic MaterialPorous
Substrate
IP Condition
(Optimum)
Polyamide
Thickness (nm)
Water Flux
(L m−2 h−1 bar−1)
Salt
Rejection
Year
[Ref]
PolyphenolsTA-Fe nano scaffoldPSF UF
substrate
(Mw 35,000)
0.2 wt% PIP/water,
0.15 wt% TMC/n-hexane 1 min reaction
54.919.620.6 ± 2.8 α
(NaCl/MgSO4)
2018
[32]
Noria–PEI solutionPSF UF
substrate
1 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
39.728>96%
Na2SO4
2018
[25]
TTSBI-PEI solutionPSF UF
substrate(Mw 70,000)
1 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
28.623.799.4%
Na2SO4
2020
[34]
PDAPSF
substrate
(Mw 35,000)
0.2 wt% PIP/water,
0.15 wt% TMC/n-hexane 1 min reaction
11614.834.4 ± 1.0 α
(NaCl/MgSO4)
2020
[20]
TA-DDSPSF UF
substrate
0.1 w/v% PIP/water,
0.1 wt% TMC/n-hexane
25 s reaction
4217.4>99%
Na2SO4
2021
[31]
Catechol-SAPSF UF
substrate
1 mg/mL PIP/water
0.1 mg/mL TMC/n hexane 30 s reaction
11013.7199.15%
Na2SO4
2021
[35]
Catechol-PEIPSF UF
substrate
10 mg/mL PIP/water
1 mg/mL TMC/n hexane 30 s reaction
3518.450.7
α(Mg2+/Li+)
2022
[33]
Ionic polymersPSS-Ca2+PSF UF
substrate
1 w/v% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
38.422.1599.3%
Na2SO4
2020
[36]
P[MPC-co-AEMA]-GAPSF substrate0.2 w/v% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
1220.496.8%
Na2SO4
2022
[40]
SPEK-CPTFE MF substrate (0.22 μm)0.1 wt% PIP/water,
0.025 w/v% TMC/n-hexane 1 min reaction
2536.398.5%
Na2SO4
2022
[37]
Quaternized crosslinked microgelsPAN UF
substrate
(Mw 50,000)
1.5 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
4410.193.4%
Na2SO4
2023
[38]
PAH-GAPSF UF
substrate
(Mw 600,000)
0.1 wt% PIP/water,
0.05 wt% TMC/n-hexane30 s reaction
812.598.9%
Na2SO4
2023
[39]
Polymeric organic acidHyaluronic acidPES MF
substrate
(0.10 μm)
0.5 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
41.529.5394.9%
Na2SO4
2022
[41]
Poly(caffeic acid)PAN UF
substrate
(Mw 80,000)
NA28417.798.5%
Na2SO4
2023
[42]
Other organic interlayersPVA-GAPES UF
substrate(Mw 150,000)
0.5 wt% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
9.631.499.4%
Na2SO4
2020
[27]
Gelatin-GAPSF UF
substrate
1 w/v% PIP/water,
0.1 wt% TMC/n-hexane
30 s reaction
4516.9599.3%
Na2SO4
2021
[43]
Poly (amidoxime)PES UF
substrate
(Mw 58,000)
0.2 wt% PIP/water,
0.1 wt% TMC/n-hexane
1 min reaction
18.225.299.2%
Na2SO4
2022
[44]
PEI/DNPs-GAPSF UF
substrate
1 wt% PIP/water, 0.1 wt% TMC/n-hexane
30 s reaction
33.331.3399.1%
Na2SO4
2022
[45]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Liu, M.; Zhang, L.; Geng, N. Effect of Interlayer Construction on TFC Nanofiltration Membrane Performance: A Review from Materials Perspective. Membranes 2023, 13, 497. https://doi.org/10.3390/membranes13050497

AMA Style

Liu M, Zhang L, Geng N. Effect of Interlayer Construction on TFC Nanofiltration Membrane Performance: A Review from Materials Perspective. Membranes. 2023; 13(5):497. https://doi.org/10.3390/membranes13050497

Chicago/Turabian Style

Liu, Mingxiang, Lei Zhang, and Nannan Geng. 2023. "Effect of Interlayer Construction on TFC Nanofiltration Membrane Performance: A Review from Materials Perspective" Membranes 13, no. 5: 497. https://doi.org/10.3390/membranes13050497

APA Style

Liu, M., Zhang, L., & Geng, N. (2023). Effect of Interlayer Construction on TFC Nanofiltration Membrane Performance: A Review from Materials Perspective. Membranes, 13(5), 497. https://doi.org/10.3390/membranes13050497

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop