Synthesis and characterization of flat-sheet thin film composite forward osmosis membranes
Research highlights
► Thin film composite forward osmosis (FO) membranes with tailored substrates were synthesized. ► The FO water flux depends on both rejection layer permeability and substrate structure. ► Finger-like pore structure is preferred over spongy-like structure for FO applications. ► The ratio increases with B/A ratio.
Introduction
Forward osmosis (FO) is an osmotically driven membrane process in which water diffuses through a semi-permeable membrane under an osmotic pressure difference across the membrane. In the FO process, both concentration and dilution of a given stream can be performed by applying a more-concentrated or less-concentrated solution on the other side of the membrane [1], [2]. Compared to conventional pressure-driven membrane separation processes such as reverse osmosis (RO) and nanofiltration (NF), FO can operate at nearly zero hydraulic pressure [1], [3]. Where a high-osmotic-pressure draw solution (DS) is naturally available or can be easily regenerated, the FO energy consumption can be potentially significantly lower than that of pressure-driven processes [1], [4]. FO is also believed to have reduced risk of membrane fouling [5], [6], [7], though further research is still required to understand the mechanisms involved [2], [8], [9], [10], [11]. In recent years, FO technology has become increasingly attractive, with potential applications for wastewater treatment [5], [6], [7], [12], biomass concentration [2], and seawater desalination [13], [14], [15], [16]. In addition, FO is also ideal for some sensitive applications where high pressure and high temperature needs to be avoided (e.g., food processing [17], [18], pharmaceutical applications [19], [20], etc.).
Despite the many interesting potential applications of the FO technology, there are some technological barriers that have yet to be overcome. One of the major problems in FO process is concentration polarization. Like pressure-driven membrane processes, FO experiences concentration polarization at the solution–membrane interface (external concentration polarization or ECP), which can be controlled by increasing cross flow or using spacers [8]. In addition, concentration polarization can occur inside the porous support layer of an FO membrane, which is known as internal concentration polarization (ICP) [11], [21], [22]. ICP, a unique problem in FO processes, arises as the water flux in FO has an opposite direction to the solute flux. This can lead to either (1) a concentrative ICP for the active-layer-facing-the-draw-solution (AL-DS) orientation, where the solutes from the feed solution (FS) accumulate in the porous support layer as a result of their retention by the active rejection layer, or (2) a dilutive ICP for the active-layer-facing-the-feed-solution (AL-FS) orientation caused by the dilution of the draw solution inside the support layer [11], [22]. In addition, ICP can be contributed by the solutes that diffuse from the high concentration DS to the low concentration FS for a low-rejection membrane [2], [11], [12]. In either case, the effective driving force (i.e., the osmotic pressure difference across the active layer) can be dramatically reduced, causing a severe reduction in the available water flux [11], [22].
Up to present, the synthesis of high-performance FO membrane is still in the early stage of its development. An ideal FO membrane shall possess high water flux and low solute flux in addition to good chemical stability [23]. Although many researchers have investigated the mechanisms of ICP [11], [12], [21], [22], [23], [24], [25], [26], there have only been a handful of studies focusing on FO membrane fabrication [23], [27], [28], [29], [30], [31], [32], [33], [34], [35], [36], [37], [38]. In parallel, commercial FO membranes are still limited in terms of both manufacturers and choice of membrane chemistries – the only FO membranes available commercially are the cellulose triacetate asymmetric membranes from Hydration Technologies Inc. (HTI, Albany, OR) [8], [11], [22]. The HTI membranes have been highly optimized in terms of the support structure to allow these membranes to achieve decent FO water flux [11], [22]. On the other hand, the rejection layers of these membranes tends to have low water permeability and limited solute retention [2], [11], [12], which means that there are still significant opportunities to further improve the FO performance.
The objective of the current study was to determine the effect of the substrate and rejection layer properties on the FO performance. In this study, thin film composite (TFC) polyamide membranes with tailored support structures were developed. Morphologies and physical characteristics of the resultant FO membranes were investigated and compared to commercial FO as well as RO membranes to illustrate the importance of both the support layer structure and the active rejection layer separation properties.
Section snippets
Chemicals and membrane materials
Unless otherwise specified, all chemicals were of analytical grade with purity over 99% and were used as received. Ultrapure water was supplied from a Milli-Q ultrapure water system (Millipore Singapore Pte Ltd) with a resistivity of 18.2 MΩ cm.
Polysulfone beads (PSf, molecular weight 75,000–81,000 Da, Solvay Advanced Polymers, LLC, GA) were used for preparing the membrane substrates. N-methyl-2-pyrrolidone (NMP, Merck Schuchardt OHG, Hohenbrunn) was used as the solvent for the casting solution.
Characterization of membrane substrates
Two TFC FO membranes, TFC-1 and TFC-2, were fabricated in the current study (Table 1), and their substrates are denoted as S-1 and S-2, respectively. The structures of these two substrates are shown in Fig. 1(a)–(d) for S-1 and Fig. 2(a)–(d) for S-2. From the SEM micrographs, both substrates had overall thickness ∼75 μm (Fig. 1, Fig. 2, and Table 2). These substrates had highly porous structures with long finger-like pores formed under a thin sponge-like skin layer (thickness <2 μm, see Fig. 1,
Conclusions
In this study, thin film composite FO membranes were synthesized. The membrane substrates, prepared by phase inversion of polysulfone, had straight finger-like pores under a thin sponge-like skin layer. The polyamide rejection layers were then formed by interfacial polymerization of TMC and MPD. The resulting FO membranes (TFC-1 and TFC-2) had small structural parameters (s = 0.67–0.71 mm) as a result of the thin cross-section, low tortuosity, and high porosity of the membrane substrates. In
Acknowledgements
The authors thank the Environment and Water Industry Programme Office (EWI) under the National Research Foundation of Singapore (Project #0801-IRIS-05) for the financial support of the work. We are also grateful to the Singapore Economic Development Board for funding the Singapore Membrane Technology Centre. Hydration Technology Inc. and Dow FilmTec are thanked for providing us free membrane materials.
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