The upper bound of thin-film composite (TFC) polyamide membranes for desalination
Graphical abstract
Introduction
Membrane-based desalination and water reuse have gained increasing popularity in arid regions to cope with water scarcity [1,2]. These applications typically use thin-film composite (TFC) reverse osmosis (RO) and nanofiltration (NF) membranes, where a thin polyamide rejection layer is synthesized on top of a porous substrate by an interfacial polymerization (IP) reaction [3]. TFC membranes with greater water permeability can significantly reduce the specific energy consumption, whereas increasing their salt rejection is beneficial to improve the product water quality [4]. Nevertheless, there exists a strong tradeoff between membrane water permeability and selectivity: increasing water permeability generally leads to reduced salt rejection [[5], [6], [7]].
Historically, the tradeoff between membrane permeability and selectively was first introduced in the context of gas separation. In 1991, Robeson [8] published his classical work on the “upper bound” for the separation factor and permeability for two-gas systems (e.g., O2/N2, CO2/CH4, etc.), which quickly became a standard benchmark for gas separation membranes. Owing to the huge success of this seminal work, Robeson [9] published a follow-up paper in 2008 to update the upper bound by including several newly developed membrane materials (e.g., ladder-type and perfluorinated polymers). To date, the 2008 Robeson's upper bound (Fig. 1a) is regarded as the golden ruler to gauge nearly all new membrane development works in the gas separation field [[10], [11], [12], [13], [14], [15], [16], [17]].
Compared to the huge success of the Robeson's upper bound in gas separation, the upper bound is much less established for desalination membranes. For example, Tang and coworkers [7] reported the tradeoff relationship between water permeability coefficient and NaCl rejection based on 11 commercial TFC polyamide RO and NF membranes. In 2011, Geise et al. [5] formalized the theoretical framework for the upper bound of desalination membranes on the basis of classical solution-diffusion theory [18] for the first time. These authors then provided a log-log upper bound plot of the intrinsic water/NaCl permeability selectivity (Pw/Ps) vs. the intrinsic water permeability Pw for a set of 26 membranes of various chemistries (Fig. 1b). In their approach, the calculation of Pw and the intrinsic NaCl permeability Ps requires the determination of the exact thickness of rejection layers, which is often challenging for TFC polyamide membrane due to the nanosized voids contained in their “ridge-and-valley” surface roughness structures [[19], [20], [21], [22]]. In a more recent review paper, Werber et al. [6] reported the tradeoff relationship in the form of water-salt permselectivity A/B vs. the water permeability coefficient A (Fig. 1c), which provides a simpler way to evaluate polyamide RO membranes. Nevertheless, all the existing attempts relied on relative small-sized data sets. A more comprehensive survey of the literature is yet to be performed to establish the state-of-the-art upper bound for desalination membranes.
In this study, we analyzed the separation performance of TFC RO and NF membranes, both commercial ones and those prepared in-house, using a dataset collected from more than three hundred of papers published in the last three decades. On this basis, we formulated their upper bound relationship, which could serve as a standard reference in the field of desalination membranes much like the Robeson's upper bound for gas separation membranes. We further examined the effect of various membrane synthesis conditions on the resulting separation performance using the upper bound as a reference framework. Our study provides a new critical tool for the evaluation of membrane development works.
Section snippets
Theoretical background
The transport of water and solutes through a dense polyamide rejection layer can be described by the solution-diffusion model [18,23,24]:where Jw and Js are the water flux and solute flux, respectively; ΔP, Δπ, and ΔC are the differences in hydraulic pressure, osmotic pressure, and solute concentration across the membrane, respectively. The water permeability coefficient A (also known as the water permeance) and solute permeability coefficient B are related to the intrinsic
The upper bound
Fig. 2 presents the dependence of NaCl transmission (1 - R) and water/NaCl permselectivity (A/B) on water permeance A based on a set of 1204 data points collected from the literature [19,20,[27], [28], [29], [30], [31], [32], [33], [34], [35], [36], [37], [38], [39], [40], [41], [42], [43], [44], [45], [46], [47], [48], [49], [50], [51], [52], [53], [54], [55], [56], [57], [58], [59], [60], [61], [62], [63], [64], [65], [66], [67],[68], [69], [70], [71], [72], [73], [74], [75], [76], [77], [78]
Monomer types
The state-of-the-art TFC RO membrane is composed of a dense crosslinked polyamide, a porous ultrafiltration support layer and a non-woven fabric layer to provide strong mechanical stability (Fig. 5a). The polyamide layer, which largely determines the water flux and salt rejection [93], is usually prepared by an interfacial polymerization reaction between m-phenylenediamine (MPD in aqueous phase) and trimesoyl chloride (TMC in organic phase, Fig. 5b). At the meantime, a wide range of alternative
Implications
The current study establishes an upper bound relationship for water permeance and water to NaCl selectivity for TFC polyamide membranes, which provides a useful tool for benchmarking future membrane development. While the effect of concentration polarization is not included in Fig. 2 due to the general limitation of literature data, additional analysis in Fig. A1 (Supporting Information Appendix A) shows that both A and A/B could be underestimated by assuming fcp = 1. Therefore, future studies
Conclusion
This study analyzed the separation properties of TFC polyamide membranes gathered from more than 300 technical papers published in the last three decades. The analysis showed a clear permeance-selectivity tradeoff between the membrane water permeance (A) and water/NaCl selectivity (A/B) for polyamide-based desalination membranes so that membranes with higher water permeance tend to have lower water/NaCl selectivity. This study further reviews the effect of various synthesis conditions (monomer
Acknowledgment
This study receives financial support from the Seed Funding for Strategic Interdisciplinary Research Scheme, the University of Hong Kong.
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