M. Obaidac,
Hend Omar Mohameda,
Ahmed S. Yasina,
Olfat A. Fadalic,
Khalil Abdelrazek Khalilde,
Taewoo Kimb and
Nasser A. M. Barakat*bc
aBionanosystem Engineering Department, Chonbuk National University, Jeonju 561-756, Republic of South Korea
bOrganic Materials and Fiber Engineering Department, Chonbuk National University, Jeonju 561-756, Republic of South Korea. E-mail: nasser@jbnu.ac.kr; Fax: +82 632702348; Tel: +82 632702363
cChemical Engineering Department, Faculty of Engineering, Minia University, Minia, Egypt
dMechanical Engineering Department, King Saud University, P.O. Box 800, Riyadh 11421, Saudi Arabia
eMaterials Engineering and Design Department, Aswan University, Aswan, Egypt
First published on 14th October 2016
A simple and novel treatment methodology is introduced to produce PVDF-based thin-film composite forward osmosis (TFC-FO) electrospun membranes for enhanced desalination performance. The proposed treatment strategy is based on improving the surface properties of the PVDF electrospun nanofiber support layer using triethylamine (TEA). The results indicated that this strategy enhanced the interfacial polymerization step by overcoming the hydrophobicity feature dilemma of the PVDF support layer. As an FO membrane, the characterization of the modified membrane shows a distinct decrease in the structure parameter of the support layer by 67%, which mitigates the adverse effect of the internal concentration polarization (ICP) by 45%. Moreover, the performance of the modified TFC-FO membrane exhibited a high water flux, approximately 68 LMH and low reverse salt flux, about 2 g m−2 h−1 at 2 M NaCl draw solution, with >99.5% salt rejection. Overall, the introduced modification technique has the advantages of being inexpensive, easy to implement, and appropriate for commercial membranes.
Basically, the FO system consists of three main parts: a draw solution (DS, high osmotic pressure), a feed solution (FS, low osmotic pressure) and a semipermeable membrane. The membrane is the heart of this process; therefore, it is responsible for the selectivity, water flux and salt rejection. Accordingly, many efforts were exerted to produce effective membranes. Several membranes have been introduced such as cellulose acetate (CA) or cellulose triacetate (CTA),6,7 polyamide and composite polyamide or thin film composite (TFC).8–10 Among the reported FO membranes, polyamide and TFC membranes exhibit excellent salt rejection, high water flux and distinct stability over a broad pH range (2–12).11 TFC membranes are composed of a thin film polyamide selective layer (PA) seated on the top of a support layer. Recently, this class of membrane has a wide prevalence as an effective FO membrane.12
The desired characteristics for optimum TFC membranes are a defect-free ultrathin selective layer with excellent permeability (high water flux) and selectivity (high salt rejection), a high porous thin support layer with small structural parameter (S) to decrease the internal concentration polarization (ICP), excellent mechanical properties, and excellent hydrophilicity to augment water flux and reduce fouling.13 The TFC membrane performance can enhanced by modifying the support layer and/or the active selective layer. For instance, to modify the active selective layer, incorporation of hydrophilic nanoparticles into a polyamide layer (PA) such as hydrophilic functionalized titanate nanotubes (TNTs),14 zeolite nanoparticles,15,16 halloysite nanotubes (HNTs)17 and TiO2 NPs18 has been carried out. In addition, the enhancement of the support layer was achieved using many polymers to fabricate the TFC membranes, such as PVDF,19 polyethersulfone,20 polytriazole-co-polyoxadiazole,21 polysulfone,22 cellulose ester,23 polyketone24 and PAN/cellulose acetate (CA) blend,25 in order to improve the support layer characteristics and augment the FO desalination process.
Among the polymers utilized for the support layer, PVDF, a semi-crystalline polymer, has emerged as an attractive polymer used for support layer fabrication due to its excellent properties such as thermal stability, chemical resistance, and mechanical properties. Unfortunately, the hydrophobicity of PVDF is a big dilemma constraining its wide application in FO desalination process.26,27 Typically, the hydrophobicity feature leads to a discrete layer of the active polyamide film because the first step in the interfacial polymerization process uses an MPD aqueous solution.
Besides the nature of the used polymer, the fabrication technique of the membrane has a vital role in the support layer performance.28 When compared to the phase inversion technique, used for membrane fabrication, electrospinning is a versatile technique to produce a class of nanofiber materials that reveals intrinsically high porosity with an interconnected pore structure, which can be used as a promising candidate for the TFC membrane support layer. Moreover, the electrospun support layer has many advantages over conventional layers fabricated using a phase inversion method such as high porosity, low structure parameter (low tortuosity, which leads to a hindered ICP) and low thickness (controlled by time or electrospun solution volume).28
Herein, to modify the wettability, the PVDF electrospun nanofiber mat was improved using a simple and highly effective modification process, involving treatment with TEA before the interfacial polymerization process. Simply, the PVDF electrospun nanofiber support layer was immersed in TEA for 1 min, and then the aqueous phase was poured onto the support surface. The treatment purpose is to achieve two objectives: (1) to create cross-linking on the support layer and (2) to enhance the support layer wettability, which allows the MPD aqueous phase to wet the support layer and consequently, fabricate a continuous and smooth PA layer. The results revealed a distinct enhancement in the TFC properties as well as a highly improved performance in the FO unit.
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Scheme 1 Interfacial polymerization of m-phenylene diamine (MPD) with trimesoyl chloride (TMC).29 |
Four different concentrations of NaCl (0.5, 1, 1.5 and 2 M) were used as a draw solution (DS) to investigate the membranes performance. Distilled water was used as a feed solution (FS). A digital balance was used to measure the decrease in the mass of the feed solution in order to compute the water flux (Jv, LMH) through the FO membrane. Moreover, the balance was connected to a PC to record the decrease in FS with time for 1 h. Conversely, the reverse salt flux (Js, g m−2 h−1) was calculated by measuring the conductivity of the FS at the beginning and the end of the test using a conductivity meter (LabQuest 2). Numerically, eqn (1) and (2) were used to calculate the water flux and reverse salt flux, respectively.30 The effective area of the membrane was 5 cm2 and all the experiments were conducted at room temperature.
![]() | (1) |
![]() | (2) |
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Furthermore, the phases of pristine PVDF and treated PVDF are shown in Fig. 2B and S1.† It is known that PVDF can be found in different phase structures. Herein, the α-phase and β-phase were found wherein the α-phase is distinguished at 762 cm−1 (CF2 bending) and 795 cm−1 (CH2 rocking), whereas the β-phase is displayed at 840 (CH2 rocking), 1276 and 1431 cm−1.35,36 As shown, the intensity of the peaks of the β-phase was decreased in the PVDF–TEA membrane due to the crosslinking in PVDF as a result of the treatment with TEA.
Moreover, the calculation method used to determine the β-phase content has been explained in our previous work.19 In brief, the intensity of the absorbance peak at 840 cm−1 for the β-phase and at 762 cm−1 for the α-phase was calculated and used in eqn (4) to estimate the amount of β-phase.37,38
![]() | (4) |
Numerically, as shown in Fig. S1,† the β-phase content decreased from 86.5% ± 3.3% in pristine PVDF to 79.4% ± 1.25% in the treated membrane due to the decrease in the absorbance intensity of the β peak at 840 cm−1, as shown in Fig. 2B.
The Raman results of the pristine PVDF support layer, in Fig. 2C, show that the peaks at ∼839 cm−1 and ∼1432 cm−1 are assigned to the β and γ bands, which are attributed to the rocking CH2 and asymmetric stretching CF2 vibrations (∼839 cm−1) and bending CH2 vibrations (∼1432 cm−1).39 Moreover, the band at 2974 cm−1 was assigned to the CH2 symmetric stretching.40 In contrast, treatment of the PVDF support layer with TEA introduced changes in the crystal structure wherein the band at ∼839 cm−1 disappeared, which is typical for the β-crystal phase. In addition, the bands at ∼2974 cm−1 and ∼1432 cm−1 also disappeared for the PVDF–TEA support layer owing to a decrease in the intensities of the crystal peaks of PVDF.39 Moreover, the band at 1696 cm−1 was attributed to CC str.33 Overall, the Raman results confirmed the change in the structure and crystallinity of the modified support layer (PVDF–TEA), which proved the formation of cross-linking in the material.
The FT-IR spectra for the TFC membranes covered with a polyamide layer are presented in Fig. 2D. As shown, the peaks at 1544 and 1616 cm−1 can be assigned to the amide II band (N–H in-plane bending and N–C stretching vibration of a –CO–NH– group) and aromatic amide (N–H) deformation vibrations,41 respectively. The stretching vibrational band at 1665 cm−1 was assigned to the CO stretching of carboxylic acids, referred to the amide I band, which was attributed to the polyamide layer.41–43 Moreover, a broad peak, appearing at 3140–3600 cm−1 and centered at 3340 cm−1, represents the N–H stretching of the primary and secondary amines.
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Fig. 3 FE-SEM images and corresponding EDX mapping of the electrospun support layer: (A and C) PVDF and (B and D) PVDF–TEA. |
Based on the aforementioned characterization, the cross-linking formed can be explained as follows: first, double bonds are formed within the polymer chain due to the elimination of the HF from the polymer. Later on, crosslinking is formed by the conjunction of these double bonds, as shown in Scheme 2, which displays a conceptual illustration of the expected mechanism. From the EDX results in Fig. 3C and D, it can be noticed that the fluorine weight percentage was reduced by 31% for PVDF–TEA, which confirmed the elimination of HF from PVDF in the presence of TEA. In addition, the changes in the crystallinity and phase structure of PVDF–TEA based on the Raman and FT-IR analysis support this finding.
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Scheme 2 The proposed mechanism of cross-linking in the PVDF–TEA support layer.39,44,46 |
It can be noted that the mechanism of dehydrofluorination and crosslinking of the fluorinated polymers in the presence of an amine, diamine and also ammonia has been previously reported.44–46
Moreover, the polyamide layer morphology was characterized by recording the SEM and FE-SEM images of the surface of the membranes after the interfacial polymerization process. From Fig. 4A and B, it can be observed that the polyamide layer was formed in both the pristine and the treated PVDF electrospun support layers. Moreover, the top surface of the polyamide layer in the case of the pristine PVDF membrane was thinner than the PVDF–TEA membrane, as shown in Fig. 4C and D. In addition, the nanofibers can be seen in the event of the pristine membrane (Fig. 4C), while the PA layer was denser in the case of the treated material. Formation of a relatively thick and continuous PA layer upon treatment with TEA was assigned to the improvement of the membrane's wettability, which will be discussed later. EDX mapping indicated that the nitrogen and oxygen contents were increased in the treated TFC membrane, as shown in the lower panels of Fig. 4C and D.
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Fig. 5 The wettability (A) and work of adhesion and the surface energy (B) of the modified and unmodified membranes before and after the activation. |
Moreover, the wettability of the top (PA layer) and bottom (support layer) surfaces of the TFC membranes was measured and plotted in Fig. 5 and S3.† The results indicate that the hydrophilicity of the modified TFC–PVDF–TEA membrane was increased for both surfaces. Numerically, the WCA was 39.56° and 81.5° for the top and support layer, respectively. On the other hand, the top surface (active layer) of the pristine TFC–PVDF membrane showed a high WCA (about 87.9°) and the bottom surface (support layer) exhibits a hydrophobic surface; the WCA was 109.3°. The enhancement of the hydrophilicity of the modified membrane was attributed to the increase in the surface energy and the work of adhesion, as shown in Fig. 5, as a result of the increase in the nitrogen and oxygen contents on the surface (Fig. 4C and D).
Furthermore, the PVDF support layer revealed a minuscule value for the surface energy as well as the work of adhesion; this was related to the fluorine atoms, which have a low surface energy. Instead, the surface energies of the top surfaces were 29.8 and 52.9 mJ m−2 for the pristine TFC–PVDF and the modified TFC–PVDF–TEA, respectively. The increase of the latter was associated with the increase in the nitrogen contents as discussed beforehand. Alternatively, the bottom surface (support layer) of the TFC–PVDF membrane displayed a high surface energy when compared to the support layer before the polymerization step; this increase was attributed to the formation of PA at some point on the bottom side of the membrane. However, the increase in the surface energy of the bottom surface (support layer) for TFC–PVDF–TEA by approximately 7 times was related to the reduction of the fluorine percentage, as shown in Fig. 3D, as well as the formation of PA at some point on the bottom. Moreover, the work of adhesion between the water and the membrane surface was measured; the results supported the surface energy data wherein the same trend was observed in the work of adhesion. Overall, the modified TFC–PVDF–TEA membrane exhibited an excellent hydrophilicity for both the polyamide and support layers. The surface energy and the work of adhesion results support and confirm this finding.
A (L m−2 h−1 bar−1) | B (L m−2 h−1) | S (μm) | R2 − Jw | R2 − Js | CV% | |
---|---|---|---|---|---|---|
TFC–PVDF | 0.98 | 0.16 | 89.7 | 0.959 | 0.975 | 9.59 |
TFC–PVDF–TEA | 0.96 | 0.03 | 29.5 | 0.993 | 0.993 | 8.2 |
From Table 1, the modified PVDF support layer (PVDF–TEA) has the lowest structural parameter (S), which enhanced the membrane performance by decreasing the ICP. Correspondingly, the salt permeability (B, L m−2 h−1) was decreased for the modified TFC membrane by 5.3 times when compared to the pristine TFC–PVDF, as shown in Table 1. On the other hand, a negligible change in the water permeability (A, L m−2 h−1 bar−1) was observed (Table 1). Overall, from these characterizations, it can be concluded that the modified TFC membrane was more suitable for FO than the pristine one.
On the other hand, the water and reverse salt fluxes (Fig. 6) were determined to evaluate the membranes using a laboratory scale FO system (Fig. 1) wherein eqn (1) and (2) were used to estimate the water and reverse salt flux values, respectively. The water flux for the pristine and modified TFC membranes are presented in Fig. 6A at various osmotic pressures (concentrations) of the draw solutions. It was observed that the modified TFC membrane has a higher water flux than the pristine TFC membrane at all the concentrations of the draw solutions studied. The water flux was increased by about 27%, 37% and 58% for the modified TFC membrane at DS concentrations of 0.5, 1 and 2 M NaCl, respectively. The high increase in the rate of water flux was related to the smallest value of ICP in the modified support layer, which will be discussed later. Likewise, the excellent water flux of the modified TFC membrane was attributed to the increase in the hydrophilicity of the support layer of the treated membrane as well as the decrease in the structural parameter. Alternatively, the reverse salt flux (Fig. 6B) observed for the modified TFC membrane was very small when compared to the pristine sample; this was due to the low salt permeability of the modified membrane, which was related to the high rejection layer. On the other hand, the reverse salt flux of both membranes was in an acceptable range.
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Fig. 6 Water flux (A) and reverse salt flux (B) of the pristine TFC–PVDF membrane and modified TFC–PVDF–TEA membrane. |
Moreover, the reverse flux selectivity (Jw/Js), which depends on both the water and salt permeability of the rejection layer, whilst independent of the draw solution concentration,47 was determined and the results presented in Fig. 7. It was notable that the modified membrane showed an excellent reverse flux selectivity wherein the average was 34 L g−1 compared to 5 L g−1 found for the pristine sample.
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Fig. 7 Reverse flux selectivity of the pristine and modified TFC membranes at different draw solution osmotic pressures. |
Herein, Ci, CDm and CFm were estimated using eqn (S1)–(S3) in the ESI† based on the Suh and Seockheon report.48 Sequentially, the drop in the osmotic pressure difference was calculated based on the difference in Ci and CDm divided by the theoretical osmotic pressure difference to estimate ICP and the results are presented in Fig. 8.
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Fig. 8 (A) The drop in the osmotic pressure difference due to ICP and (B) the theoretical, experimental and calculated (based on the ICP) water flux. |
From the results in Fig. 8A, it was observed that the difference in the osmotic pressure decreased by 25.5% for the TFC–PVDF membrane at 0.5 M of the DS and the percentage of the drop increases by increasing the draw solution concentration wherein it reaches to 50% at 2 M DS. In contrast, TFC–PVDF–TEA shows a smaller drop in the osmotic pressure difference than the pristine sample. Moreover, an increase in the draw solution concentration for TFC–PVDF–TEA also increases the drop percentage of the pressure difference; numerically decreased by 11.7% and 30.6% for the 0.5 M and 2 M draw solutions, respectively.
However, the ICP has the significant effect of the diminution of the pressure difference, whereas the external concentration polarization (ECP) has a negligible value in this case because the feed was distilled water. Therefore, no concentrative ECP and a slight dilutive ECP (0.7% and 1.1% for PVDF and PVDF–TEA, respectively) was carried out due to the low cross velocity.
The osmotic pressure profile is plotted in Scheme 3 (right) and used to determine the ICP effect on the osmotic pressure. The osmotic pressure of 2 M NaCl DS decreased by 51.2% at the interface; numerically from 99.11 to 48.4 bar for the TFC–PVDF membrane, while the drop was 31.7% for the TFC–PVDF–TEA membrane.
The theoretical water flux, based on the product of the water permeability, and the difference in the theoretical osmotic pressure, were calculated and compared with the experimental results as well as the results computed based on the concentration polarization CP (using the difference between Ci and CFm), as shown in Fig. 8B. The results of the experimental and those calculated based on the CP were almost identical and less than the theoretical results. This demonstrates the influence of the CP on the decrease of the water flux and the performance of the FO membrane. Furthermore, a drop from 24% to 54% (for 0.5 M and 2 M, respectively) in the water flux was observed for TFC–PVDF. However, the TFC–PVDF–TEA membrane shows less water flux drop than the pristine sample numerically from 5% to 30% at 0.5 M and 2 M, respectively; this was related to the decrease in the ICP due to the smallest structural parameter. Overall, the decrease in the structural parameter has a strong effect on the ICP as well as the water flux wherein the increase or decrease in the structural parameter shows an increase or decrease in the actual path through the membrane support layer (tortuosity), which has a negative or positive effect, respectively.
Moreover, an increase in the hydrophilicity of the support layer enhanced the passing of water. The hydrophilic support layer allows the draw solution to wet its surface easily and this leads to passing the draw solution through the support layer, making an almost real osmotic pressure at the inner surface of the polyamide layer, which correspondingly enhances the passing of water from the feed to the draw solution.
Overall, both the TFC–PVDF and TFC–PVDF–TEA have a low reverse salt flux value, which points out that electrospinning is a very successful process to prepare the FO membrane. Moreover, the modified TFC membrane has the highest water flux value and reveals an acceptable range of reverse salt flux. Therefore, the two membranes exhibited an excellent salt rejection (>99%) as calculated based on eqn (3); this was related to the polyamide layer on the membrane surface wherein it is known that the polyamide layer has an excellent salt rejection.
Based on the obtained results, it can be concluded that the PVDF–TEA support layer is optimal to synthesize a TFC-FO electrospun membrane with promising performance, including a high water flux, excellent salt rejection, and low reverse salt flux.
Likewise, in order to evaluate the introduced membrane properly, a comparison with other reported FO membranes is presented in Table 2. From the table, the modified TFC–TEA membrane achieved the highest water flux as well as the lowest (Js/Jv) ratio when compared to the other membranes. Overall, the introduced study reports a new technique that can be used to enhance FO membrane performance as well as opening new opportunities for using the electrospinning technique for the preparation of effective electrospun membranes used in FO desalination technology.
In summary, a novel treatment technique for PVDF via a chemical modification method using triethylamine has been successfully introduced in this work. Moreover, the results of the modified TFC-FO membrane reveal a very high water flux with excellent salt rejection and very low reverse salt flux, which results in the lowest structure parameter reported to date, high water permeability, low salt permeability as well as low ICP.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c6ra18153h |
This journal is © The Royal Society of Chemistry 2016 |