Research Article pubs.acs.org/journal/ascecg
Meldrum’s Acid Modified Cellulose Nanofiber-Based Polyvinylidene Fluoride Microfiltration Membrane for Dye Water Treatment and Nanoparticle Removal Deepu A. Gopakumar,†,‡ Daniel Pasquini,§ Mariana Alves Henrique,§ Luis Carlos de Morais,∥ Yves Grohens,‡ and Sabu Thomas*,† †
International and Inter University Centre for Nanoscience and Nanotechnology, Mahatma Gandhi University, Kottayam, Kerala 686560, India ‡ IRDL-FRE CNRS 3744, Universite de Bretagne Sud, Lorient 56100, France § Chemistry Institute, Federal University of Uberlandia−UFU, Av. João Naves de Á vila, 2121, Campus Santa Mônica, Bloco 1D, 38400-902, Uberlândia-MG, Brazil ∥ Universidade Federal do Triângulo Mineiro (UFTM), Av. Doutor Randolfo Borges, 1400, Secretaria do ICENE−SALA 109, Uberaba, MG, Brazil ABSTRACT: The work presented here aims to study and compare the performance of a polyvinylidene fluoride (PVDF) electrospun membrane, unmodified cellulose nanofiber (CNF) based PVDF membrane, and Meldrum’s acid (2,2-dimethyl1,3-dioxane-4,6-dione) modified CNF-based PVDF membranes against the Fe2O3 nanoparticle filtration and crystal violet (CV) dye adsorption. Herein, we introduced a facile method to produce a unique green adsorbent material from cellulose nanofibers (CNFs) via a nonsolvent assisted procedure using Meldrum’s acid as an esterification agent to enhance the adsorption toward positively charged crystal violet dyes. Most of the surface modifications of cellulose nanofibers have been done using toxic organic solvents like pyridine, dimethyl acetate, (2,2,6,6-tetramethylpiperidin-1-yl)oxyl (TEMPO), etc. So far, this is the first report on the surface modification of cellulose nanofibers via a nonsolvent assisted procedure. Both CNF-based PVDF membranes were prepared by successive coating of modified and unmodified CNFs on to the surface of a PVDF electrospun membrane. All the demonstrated membranes showed high filtration capacity against the Fe2O3 nanoparticles. With the 10 mg/L of crystal violet (CV) aqueous solution, CV adsorption of PVDF electrospun membrane, and unmodified CNF-based PVDF membrane was around 1.368 and 2.948 mg/g of the membrane respectively, whereas it was 3.984 mg/g of the membrane by Meldrum’s acid CNF-based PVDF membrane. The demonstrated Meldrum’s acid modified CNFbased PVDF membrane was proven to be the efficient media that can concurrently eliminate the Fe2O3 nanoparticles and CV dyes from the water. The investigation into the surface chemistries of cellulose nanofibers beyond the adoption of toxic solvents can enhance the economic usefulness of the process and also yield a new ecofriendly adsorbent material that is agreeable to adsorbing various toxic pollutants. KEYWORDS: Cellulose nanofiber, Electrospinning, Meldrum’s acid, Dye adsorption, Nanoparticle removal techniques.2−6 From these mentioned methods, microfiltration (MF), ultrafiltration (UF), and nanofiltration (NF) using pressure driven technologies have gained considerable interest due to their impressively high performance and low cost.7,8 These conventional ultrafiltration, nanofiltration, and microfiltration membranes for water purification are produced by phase immersion methods like immersion precipitation and thermally induced phase separation, where the torturous path
1. INTRODUCTION All plants and animals must have water to survive. With the evolution of various industries, water pollution is one of the biggest problems that the world faces. After agriculture, the textile dyeing and finishing industry has generated a large water pollution problem as most of the chemicals coming from these industries are highly toxic and directly or indirectly affect human health. Since the development of advanced modern textiles and the arrival of new synthetic dyes to the market daily, water pollution due to dye waste is an important issue to study.1 Biological processes, chemical processes, and the operation of electromagnetic radiation are common removal © XXXX American Chemical Society
Received: December 5, 2016 Revised: December 29, 2016
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DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
Research Article
ACS Sustainable Chemistry & Engineering results in the low water flux. Electrospun membranes have some advantages over the membranes produced via phase immersion methods such as higher effective porosity with continuously interconnected pores, light weight, and high surface area.9,10 Therefore, electrospinning is a promising technique for generating continuous fibers with diameters in the range of a few hundred nanometers.11 They exhibit excellent mechanical strength, water flux, and particle rejection. These properties make electrospun membranes an excellent platform for microfiltration applications.12 On the other hand, the average porosity of the electrospun membrane is too high to remove smaller objects like viruses and textile dyes by size exclusion.13,14 So, to eliminate the minute particles like viruses and textile dyes, an additional adsorption mechanism is essential without affecting the permeability of electrospun MF membranes. One of the typical approaches to remove viruses or dyes from wastewater is to increase the electrostatic charges of the MF membrane to enhance the absorption capability.15 PVDF (polyvinylidene fluoride) has earned great attention in recent years as a membrane material due to its excellent properties like high thermal stability, mechanical strength, and chemical resistance toward solvents, acids, and base. Compared to other fluoropolymers PVDF can quickly dissolve in most of the organic solvents. These outstanding properties make PVDF membranes have been used as membrane filters for water purification.16−22 Nanomaterials play a significant role in developing new materials with high efficiency at low cost for water pollution. Among the nanomaterials, cellulose nanofibers (CNFs) are one of the promising adsorbent materials for water purification due to their low cost, abundant hydroxyl groups, natural abundance, and ecofriendly nature. Moreover, the CNFs have the enormous amount of surface hydroxyl (OH) groups, which enables a lot of surface chemistries or incorporation of chemical groups that may increase the adsorption toward the various pollutants in water. Until now, a few extensive reports have been published in the area of water purification using nanocellulose by Ma et al.3,5 Most of the works based on nanocellulose in water treatment were reported by the Chemistry Department of Stony Brook University, USA. They demonstrated nanocellulose based membranes for the removal of positively charged dyes, bacteria, and viruses from water. They used (2,2,6,6-tetramethylpiperidin-1-yl)oxyl (TEMPO) oxidation surface treatment for cellulose nanofibers for almost all of their studies. An obvious disadvantage of this oxidation procedure is the use of TEMPO and sodium bromide, which both are associated with environmental issues. Moreover, the TEMPO reagent is very expensive to commercialize in the industry level. Another work was done by Qiao et al., and they removed cationic dyes using carboxylate functionalized cellulose nanocrystals. They used pyridine as a solvent medium for the carboxylation of cellulose nanocrystals, which is highly toxic in nature.23 Cao et al. removed silica nanoparticles from the water using poly(acrylonitrile) nanofibrous membrane reinforced with jute cellulose nanowhiskers, where they used TEMPO surface treatment for the cellulose nanowhiskers.24 So there is every need to formulate new chemical design protocols on the surface treatment of cellulose nanofibers via a solvent free procedure technique. In this context, we intended to produce a unique adsorbent material from cellulose nanofibers (CNFs) via nonsolvent assisted method using Meldrum’s acid as an
esterification agent which can remove the dyes from water. To the extent of our knowledge, preparation of new green based adsorbent to adsorbing dyes from CNFs via a nonsolvent assisted procedure using Meldrum’s acid as esterification agent has not been addressed to date. This finding offers a new platform for the surface treatment of cellulose nanofibers using solvent free green technology.
2. EXPERIMENTAL SECTION 2.1. Materials and Methods. Sunflower stalks were procured from Umbria, Italy. PVDF with Mw (275 000 g/mol), 2,2-dimethyl1,3-dioxane-4,6-dione (98%) (Meldrum acid), and iron oxide (Fe2O3) nanoparticles, 50−100 nm particle size, were procured from SigmaAldrich, Brazil, while crystal violet dye (CV, C25H30N3Cl, λmax = 584 nm, Mw = 407.98 g/mol) was procured from vetec (Brazil). Extraction of Cellulose Nanofibers from the Sunflower Stalks. A laboratory autoclave (KAUC-A1) was employed for the extraction of cellulose nanofibers (CNFs) from sunflower stalks. Mild acid hydrolysis combined with steam explosion procedure was used to extract CNFs. First, the powdered sunflower stalks were treated with alkaline solution (5 wt % of NaOH) at 180 °C in an autoclave for 90 min. Then bleaching was followed by the alkali treatment where the alkali treated sample was treated with 5 wt % of sodium hypochlorite solution for 90 min. Bleaching treatment of sunflower stalks with sodium hypochlorite solution was repeated in an autoclave until the sample became a white color. After bleaching, the sample was undergone mild acid hydrolysis where 5 wt % of oxalic acid was employed together with steam explosion under a pressure of 137 Pa in an autoclave for 20 min. Finally, the residue was washed with distilled water via repetitive centrifugation. 2.2. Preparation of PVDF Electrospun Membrane. PVDF pellets (17 wt%) were dissolved in the solvent mixture of DMF:acetone at a volume ratio of 60:40 at 50 °C. The PVDF nanofibrous electrospun membrane was prepared at 15 kV in a relative humidity of 60% at 28 °C at a feed rate of 1 mL/h with a constant tip to collector distance at 15 cm using electrospinning unit (HOLMARC HO-NEV-02). After the electrospinning process, the electrospun membrane was placed in a hot air oven at 150 °C for 3 h to remove any residual solvent and to improve the membrane overall structural integrity before any characterization was performed. 2.3. Modification of the Cellulose Nanofibers with Meldrum’s Acid. Initially, CNFs (1.3 g) and Meldrum’s acid (1.3 g) were mixed in a mortar and added to a round-bottom flask provided with the reflux condenser and the whole mixture was heated at 110 °C for 4 h in an oil bath with constant magnetic stirring. After the reaction, the resultant mixture was washed with deionized water and acetone to remove the nonreacted Meldrum’s acid and then dried in an oven at 90 °C for 1 h. After this, the Meldrum’s acid modified CNFs were subjected to FTIR and XRD analysis. 2.5. Fabrication of PVDF/Unmodified CNF-Based Nanofibrous MF Membranes and PVDF/Meldrum-Modified CNFBased Nanofibrous MF Membranes. The electrospun PVDF membrane sample in the pattern of a circular shape with 2 cm width was clamped in a glass filter filtration assembly (Holder-47 mm), where a 0.1 wt % concentration of Meldrum acid modified CNFs or unmodified CNFs, pH 7.0, was impregnated into the PVDF electrospun membrane by applying pressure, 200 mm of Hg. Then the sample was heated at 100 °C in an oven for 15 min to start the cross-linking reaction to immobilize the CNF network. The thickness of the prepared membrane was calculated using a thickness gauge (7301 MITUTOYO), and it was 170 ± 2 μm. 2.6. Transmission Electron Microscopy. A JEOL JEM 2100 transmission electron microscope (TEM) was employed to evaluate the diameter of the prepared CNFs. The diluted CNF suspension was sonicated for 7 min to avoid agglomeration and directly dropped on the copper grid for characterization. 2.7. Scanning Electron Microscopy. The morphology of PVDF electrospun membrane and nanofibrous MF membranes was examined B
DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
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Figure 1. TEM image and diameter frequency distributions of cellulose nanofibers extracted from sunflower stalks.
Figure 2. SEM image and diameter frequency distributions of PVDF electrospun membrane. using an SEM (Carl Zeiss, EVO MA10). The samples were sputtered with gold in an argon atmosphere. 2.8. X-ray Diffraction Analysis. XRD patterns were employed to check whether the Meldrum’s acid modified CNFs preserve their cellulose I structure. For that, the XRD patterns of unmodified CNF and Meldrum’s acid modified CNF was obtained with (Shimadzu XRD-6000). The XRD patterns were collected from 2θ = 5−38° at a scan rate of 2°/min. 2.9. Fourier Transform Infrared Spectroscopy. The IR spectra of CNF and Meldrum’s acid modified CNF was recorded using (IR prestige-21, Fourier transform infrared spectrophotometer, Shimadzu). The KBr disk method was employed for obtaining the IR spectra of both powdered samples from 400 to 4000 cm−1. 2.10. Water Contact Angle Studies. Water contact angles of electrospun PVDF membrane, PVDF/unmodified CNF nanofibrous MF membrane, and PVDF/Meldrum’s acid modified CNF nanofibrous MF membrane was measured using SCA20 contact angle analyzer. We used 10 μL of deionized water for the measurements. Three measurements were obtained for each sample and the average value was calculated. 2.11. Determination of the Surface Area of Membranes. A Micrometrics surface and pore size analyzer (ASAP2020) was used to conduct N2 adsorption−desorption experiments at 77 K. Before the
experiment, the sample was degassed at 573 K for 18 h. The surface area was obtained using the BET model. 2.12. UV−visible Spectrophotometer. Nanoparticle and dye removal were monitored with (Femto Mod. 800X I) by transmittance, absorbance, respectively. For the evaluation of the nanoparticles removal, the feed solution and filtrate were poured into a PMMA disposable cuvette and transmittance was obtained from 300 to 900 nm while for the assessment of dye removal, the starting and filtrate solution were poured into the PMMA cuvette and absorbance was measured at 590 nm. To calibrate the transmittance and absorbance of the samples, the spectrum of a cuvette filled with water was employed as the reference. Ultraviolet−visible spectroscopy (UV−vis) procedure was applied for the determination of solute concentrations in the starting and final solutions. 2.13. Evaluation of Adsorption Efficiency of Nanofibrous MF Membranes against Positively Charged Dyes. We used crystal violet (CV) dye as a model in this study. The evaluation of the adsorption efficiency of the nanofibrous MF membranes was done by using the following method. Initially, 0.05 g of unmodified CNF based PVDF nanofibrous MF membrane, Meldrum’s acid modified CNF based PVDF nanofibrous MF membrane and PVDF membrane was immersed in 25 mL of CV aqueous solution (10 mg/L, pH 7.0) on a shaking bed for 10−240 min at ambient temperature. The adsorption efficiency of CV dye was measured as a function of time. The C
DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
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Figure 3. Strategy for the preparation of the Meldrum’s acid modified cellulose nanofiber.
Figure 4. FTIR spectra of Meldrum modified CNF and CNF. concentration of the CV dye adsorbed on to the membrane was obtained from the concentration change of the CV solution before and after the adsorption steps using UV−visible spectrophotometer by optical adsorption at 590 nm. 2.14. Microfiltration Performance of the Nanofibrous MF Membranes. The microfiltration test of the nanofibrous membranes was carried out in glass filter filtration assembly (Holder-47 mm) with a filtration area of 9.6 cm2. Fe2O3 nanoparticles (0.2 wt %) with sizes of 50−100 nm were set as the feed solution. The microfiltration was conducted at a pressure of 200 mm Hg.
3.2. Characterization of Meldrum’s Acid Modified CNFs. After the esterification modification by Meldrum’s acid on the CNFs, the COOH groups were attached to the CNFs surface (Figure 3) which enables the adsorption of the positively charged species like crystal violet dye on to the surface of the modified CNFs. 3.2.1. FTIR Spectroscopy Studies. The IR spectra of unmodified CNFs and Meldrum’s acid modified CNFs are shown in Figure 4. From this figure, it is clearly shown that the following changes have occurred in the IR spectra of Meldrum’s acid modified CNFs when compared with CNFs. (1) The presence of the band at 2954 cm−1 is regarded as the asymmetric stretching of methylene (CH2) groups, due to the interaction between the malonyl groups and CNFs. (2) A strong band emerges at 1748 cm−1 for Meldrum’s acid modified CNFs, attributed to the presence of ester groups formed during the esterification reaction between the malonic acid and CNFs. (3) The band emerging at 1384 cm−1 for Meldrum’s acid modified CNFs indicates the presence of carboxylate groups. From this FTIR spectrum, it can be concluded that the esterification reaction between Meldrum’s acid and CNFs was successful.28 3.2.2. XRD Studies. The XRD patterns of the neat CNFs and Meldrum’s acid modified CNFs are shown in Figure 5. Two characteristic peaks at 2θ = 16.3° and 2θ = 22.6° are observed from the XRD pattern of neat CNFs, which shows the cellulose type I structure.29 From the X-ray diffraction pattern, it is clearly shown that Meldrum’s acid modification has been affected mainly by the surface hydroxyl groups of cellulose. The XRD profiles of the Meldrum’s acid modified CNF are representative of a plant-derived cellulose I structure, indicating that the cellulose type I structure is preserved even after the surface modification by Meldrum’s acid. The crystallinity indices (CrI) of the Meldrum’s-modified CNF and CNF
3. RESULTS AND DISCUSSION 3.1. Morphology of Cellulose Nanofibers and PVDF Electrospun Membrane. Transmission electron microscopy (TEM) was employed to investigate and measure the morphology and average fiber diameter respectively of the prepared CNFs from the sunflower stalks. From the TEM image, Figure 1, we can evaluate the size range of the fibers (5− 10 nm in diameter). From this image, it is clearly evident that the combination of steam explosion and mild acid hydrolysis is an efficient technique to prepare cellulose nanofibers. Chirayil et al. and Cherian et al. extracted cellulose nanofibers from isorafibers and banana leaf fibers respectively via steam explosion technique. They obtained cellulose nanofibers with the average diameter of 10−20 and 15 nm from isorafibers and banana fibers, respectively.25,26 It was anticipated that during steam explosion technique the lingo cellulosic structure undergoes chemical decomposition.27 Figure 2 showed the SEM images of PVDF electrospun membrane. From the figure, the nanofibrous membrane showed the three-dimensional arrangement of nanofibers with an average fiber diameter of 700 nm. It could be seen that from the SEM figure, nanofibrous membranes with irregular fiber arrangement of PVDF nanofibers. D
DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
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wt % of Meldrums’ acid modified CNFs (pH 7.0) into the PVDF electrospun membrane. Compared with the PVDF electrospun membrane this coating of modified CNFs resulted in a substantial enhancement in the surface area around 11.4%, i.e. from 4.6713 to 5.2078 m2/g for the PVDF electrospun membrane and Meldrum-modified CNF-based PVDF nanofibrous MF membrane, respectively, from the BET measurements. This increase in the area can improve the efficiency of the adsorption process. 3.5. Contact Angle Studies. The water contact angle measurements for the PVDF electrospun membrane, Meldrum’s acid-modified CNF-based PVDF membrane, and unmodified CNF-based PVDF membrane were measured. The water contact angle obtained for the PVDF electrospun membrane, Meldrum’s-modified CNF-based PVDF membrane, and unmodified CNF-based PVDF membrane were 142.6°, 123°, and 121° respectively. The water contact angles for both modified CNF and unmodified CNF membranes were decreased to 123° and 121°, respectively, which indicates the enhancement of the wettability of both nanofibrous membranes compared to the PVDF electrospun membrane. It can be noticed that there was only a slight difference between the contact angles of both nanofibrous membranes. The water contact angle measurements confirmed that the fouling problem of the PVDF electrospun membrane could be decreased to some extent by the coating of modified CNFs and unmodified CNFs on to the surface of the PVDF electrospun membrane. 3.6. Evaluation of the Adsorption Capacity of a Nanofibrous Membrane against Crystal Violet Dye. In this study, we used crystal violet (CV) dye as a model of positively charged particles to evaluate the adsorption efficiency of all membranes. To determine the adsorption efficiency, UV− vis spectroscopy was employed. Figure 7 illustrates the
Figure 5. X-ray diffraction pattern of Meldrum modified CNF and CNF.
samples were evaluated by using the method of Segal, as given in eq 130 CrI = [(I200 − IAM)/I200] × 100
(1)
In eq 1, CrI expresses the relative degree of crystallinity, I200 is the maximum intensities of the 200 lattice diffraction at 2θ = 23°, and IAM is the intensity of diffraction at 2θ = 18°. I200 represents both crystalline and amorphous regions, while IAM represents only the amorphous portion. The obtained crystallinity index values of Meldrum modified CNFs and CNFs were 63% and 78%, respectively 3.3. Morphology of Modified CNF-Based PVDF Nanofibrous MF Membrane. Figure 6 showed the SEM images of
Figure 6. SEM image of the top view of the Meldrum’s acid modified CNF based PVDF nanofibrous MF membrane (the uncoated membrane part is displayed on the right side).
the top view of the modified CNF-based PVDF nanofibrous MF membrane. The top modified CNF coating seems to be a relatively soft and regular surface which has a higher tendency to remove the trapped foreign particles on the surface, thus enhances the antifouling property of the membrane. Since modified CNFs are very much smaller than the PVDF fibers, at lower magnification, the cellulose nanofiber layer seems to be like the soft thin film. From this, it can be concluded that modified CNFs have been successfully coated over the PVDF electrospun membrane resulting in a nanofibrous microfiltration membrane. 3.4. Surface Area of Nanofibrous MF Membrane. Fabrication of Meldrum’s acid modified CNF based PVDF nanofibrous MF membrane was done by impregnation of 0.1
Figure 7. Adsorption capacity of PVDF membrane alone, PVDF/ unmodified CNF membrane, and PVDF/modified CNF membranes against time.
adsorption efficiency, of 10 mg/L CV by PVDF membrane alone, unmodified CNF-based PVDF membrane, and Meldrum’s-modified CNF-based PVDF membranes toward crystal violet (CV) dye as a function of time. From the figure it was clearly shown that, with the 10 mg/L of CV aqueous solution, CV adsorption of PVDF electrospun membrane and unmodified CNF-based PVDF membrane was around 1.368 and 2.948 mg/g of the membrane, whereas it was 3.984 mg/g E
DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
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3.7. Microfiltration Performance of Nanofibrous MF Membrane against Nanoparticles. Figures 9, 10, and 11 show the SEM images of the PVDF membrane alone, unmodified CNF-based PVDF membrane, and Meldrum’s acid modified CNF-based PVDF membranes respectively, top and bottom surfaces, after the removal of Fe2O3 nanoparticles. The top surfaces of the all filtrated membranes showed that the Fe2O3 nanoparticles are formed like clusters on the top of the membranes as illustrated in Figures 9a, 10a, and 11a, whereas on the bottom surfaces of all membranes, as shown in Figures 9b, 10b, and 11b, we could not find many Fe2O3 nanoparticles. These results indicate that the removal of Fe2O3 nanoparticles was similar for all membrane samples studied. Since the work was focused on the Meldrum’s-modified CNF-based PVDF membrane, we studied the UV−visible spectra of the starting (feed) and final (filtrate) solution of the Meldrum’s acidmodified CNF-based PVDF membrane, which is given in Figure 12. Figure 12 illustrates UV−vis spectra of both starting (feed) and final (filtrate) solution of for Fe2O3 nanoparticles. From the final solution, it could be seen that the Fe2O3 nanoparticles were effectively eliminated from the starting solution by the Meldrum’s-modified CNF-based PVDF membrane and the membrane had a good particle rejection ratio against the Fe2O3 nanoparticles.
of the membrane by Meldrum’s acid CNF-based PVDF membrane. These observations were comparable with those of Ma et al., who found that the adsorption of positively charged CV dye was 3.8 mg/g of the membrane using a poly(acrylonitrile) (PAN) scaffold nanofibrous membrane with cellulose nanowhiskers.23 It was found that the adsorption efficiency of Meldrum’s-modified CNF-based PVDF nanofibrous MF membrane was higher than that of PVDF electrospun membrane and unmodified CNF-based PVDF microfiltration membrane. This enhancement in the dye adsorption of the Meldrum’smodified CNF-based PVDF membrane can be justified by the high electrostatic attraction between the positively charged CV dyes and carboxylate groups (negatively charged) on the Meldrum’s acid-modified CNFs (mechanism shown in Figure 8). The adsorption of CV on to the Meldrum’s acid-modified
4. CONCLUSIONS We have prepared a new adsorbent material for the adsorption of positively charged crystal violet dyes from CNFs via a nonsolvent- assisted methodology using Meldrum’s acid as an esterification agent. It is also demonstrated that the Meldrum’smodified cellulose nanofiber-based PVDF nanofibrous membrane can be successfully used to remove the crystal violet dyes and Fe2O3 nanoparticles (with rejection of over 99%) from water. It has been shown that with 10 mg/L of crystal violet aqueous solution, CV adsorptions of the PVDF electrospun membrane and unmodified CNF-based PVDF membrane were around 1.368 and 2.948 mg/g of the membrane respectively; whereas, it was 3.984 mg/g of the membrane by the Meldrum’s acid CNF-based PVDF membrane. The Meldrum’s acidmodified CNF-based PVDF membrane showed two or three times higher adsorption than the PVDF electrospun membrane because of the high electrostatic attraction between the positively charged CV dyes and carboxylate groups (negatively charged) on the surface of Meldrum’s acid modified CNFs. This demonstrated that the membrane is unique as it can concurrently eliminate crystal violet dyes and Fe2O3 nanoparticles from water. So it is auspicious for use in water
Figure 8. Schematic representation of crystal violet removal by Meldrum’s acid-modified CNF-based PVDF nanofibrous MF membrane and its mechanism.
CNF-based PVDF membrane reached equilibrium after 3 h. Therefore, it can be concluded that the adsorption efficiency (using 10 mg/L CV aqueous solution) of the Meldrum’smodified CNF-based PVDF membrane was about two to three times higher than that of PVDF electrospun membrane. Therefore, the demonstrated membrane is expected to be a very promising adsorbent for dye wastewater treatment and dynamic adsorption in practical applications.
Figure 9. SEM images of the top surface (a) and the bottom surface (b) of the PVDF electrospun membrane after filtration of Fe2O3 nanoparticles. F
DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
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Figure 10. SEM images of the top surface (a) and the bottom surface (b) of the unmodified CNF-based PVDF electrospun membrane after the filtration of Fe2O3 nanoparticles.
Figure 11. SEM images of the top surface (a) and the bottom surface (b) of the Meldrum’s acid-modified CNF-based PVDF electrospun nanofibrous membrane after the filtration of Fe2O3 nanoparticles.
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AUTHOR INFORMATION
Corresponding Author
*E-mail:
[email protected]. ORCID
Sabu Thomas: 0000-0003-4726-5746 Notes
The authors declare no competing financial interest.
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ACKNOWLEDGMENTS This work was financially supported by India-Brazil Bilateral Scientific Cooperation MCTI-CNPq/DST (India, project 401051/2013-7) and is a collaboration research project of ́ members of the Rede Mineira de Quimica (RQ-MG) supported by FAPEMIG (project CEX-RED-00010-14). The authors gratefully acknowledge support from the International and Inter University centre for Nanoscience and Nanotechnology, Mahatma Gandhi University, India, Federal University of Uberlandia, Brazil, and Laboratoire d’Ingénierie des MAtériaux de Bretagne, Centre de Recherche Rue Saint Maude, France.
Figure 12. UV−visible spectra of feed and filtrate solution of Fe2O3 nanoparticles for the Meldrum’s acid-modified CNF-based PVDF membrane.
treatment applications. All the experimental results suggested that the Meldrum’s-modified CNFs were a promising additive for modifying the MF membrane. Moreover, this study opens up a new platform for the surface modifications of cellulose nanofibers via solvent-free techniques, which can enhance the economic feasibility of the process.
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REFERENCES
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DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
Research Article
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DOI: 10.1021/acssuschemeng.6b02952 ACS Sustainable Chem. Eng. XXXX, XXX, XXX−XXX
