Advances in Polymer Technology

Advances in Polymer Technology / 2019 / Article

Research Article | Open Access

Volume 2019 |Article ID 2345631 | 9 pages | https://doi.org/10.1155/2019/2345631

Investigations on Amphoteric Chitosan/TiO2 Bionanocomposites for Application in Visible Light Induced Photocatalytic Degradation

Academic Editor: Camino Giovanni
Received14 Oct 2018
Revised03 Apr 2019
Accepted19 May 2019
Published17 Jul 2019

Abstract

The present investigation reports the greener synthesis and characterization of novel acrylic acid grafted amphoteric chitosan/TiO2 (CAT) bionanocomposites using ultrasonic radiations. This was done by grafting of acrylic acid onto chitosan in the presence of potassium persulfate by free radical polymerization reaction. The uniform distribution of metal oxide in CA/TiO2 nanocomposites was achieved on grafted acrylic acid/chitosan which contains a weak anionic group (-COOH) using ultrasonication technique. Physiochemical techniques such as X-ray diffraction (XRD), field emission scanning electron microscope (FE-SEM), Fourier Transform Infra-Red spectroscopy (FT-IR), Energy Dispersive X-ray spectroscopy (EDX), and Thermal Gravimetric Analysis (TGA) were employed to characterize synthesized CAT. Nanocomposite CAT was applied for degradation of industrial dye. Malachite green (MG) often presents in the waste waters. The degradation kinetics were studied by monitoring the photocatalytic reaction for degradation of MG under visible light, and the rate constant of the reaction was found to be 7.13x10−3min−1. The current research work opens vistas for the new dimensions in the area of water treatment by solving the issues related to degradation reaction efficiency in visible light and cost effectiveness.

1. Introduction

The synergy between organic and inorganic materials offers the potential for the development of new generation innovative organic-inorganic composites with diversified applications in various areas such as catalysis, photo catalysis, separation technology, energy storage, and drug delivery [13]. The inorganic materials impart increased mechanical strength and thermal and chemical stability while retaining the flexibility of organic component. The hybrid materials show better electrical, chemical, or biochemical properties along with improvement in selectivity. Inorganic materials such as metal/metal oxide particles-Al2O3, Fe3O4, ZrO2, TiO2, carbon-based nanomaterials, zeolites, and silica [47] in nanocomposites can create symbiosis or multifunctional effects. The formation of nanocomposites by incorporating metal/metal oxide/metal sulphide nanoparticles into the polymeric materials has been emerged as focus area of research.

Chitin is the second most abundant polysaccharide after cellulose that consists of β-(1-4)-2-acetamido-2-deoxy-d-glucose units. Polyaminosaccharide chitosan, a copolymer of 2-amino-2-deoxy-D-glucopyranose and 2-acetamido-2-deoxy-D-glucopyranose units having β (1-4) [8] linkages, is obtained by the deacetylation of chitin. Chitosan in an acidic solution behaves as cationic polyelectrolyte and forms complexes with a large number of negatively charged species such as proteins, anionic polymers, and drugs.

Nanocomposites are materials which consist of two components, with one of them having dimensions in nanometers (10−9 m) range. Organic-inorganic nanocomposite materials are not the simple physical mixtures, but intimately linked via weak interactions/bond or strong interactions/covalent bond. These interactions have a profound effect on the material properties, in particular at the interface interaction, as well as on inner interfaces. TiO2 semiconductor is a well-known photocatalyst in the research field of energy and environment because of its unique properties like high efficiency, low cost, chemical and physical stability, noncorrosive nature, and widespread availability [911].

The band gap of TiO2 is 3.2 eV for anatase and 3.0 eV for rutile phase and requires more energy for photo excitation which is feasible only by absorption of photons of UV region. Thus, TiO2 can utilize only 5% of the entire solar spectrum, which led to its restricted application in the area of solar photocatalysis. Three fundamental approaches adopted to enhance photocatalytic activity in the visible region are (i) extension of excitation wavelength, (ii) band gap tuning, and (iii) extending charge-carrier recombination time. The different routes to achieve these parameters involve (1) surface chemical modification, (2) doping of photocatalyst (metal or nonmetal doping), and (3) coupling of semiconductor systems [1218].

The detailed literature study reveals the chitosan-polyacrylic acid materials were prepared using microwave, high temperature, or radiations induced synthesis, and their applications as super adsorbent, for removal of cations, for controlled release of drugs, and as magnetic nanospheres have been explored [1922]. The polymer based nanocomposites such as poly(vinyl alcohol)/polyacrylic acid/TiO2/graphene oxide have been used for photocatalytic degradation of pollutants [23]. Poly(vinyl alcohol)/poly(acrylic acid)/carboxyl-functionalized graphene oxide nanocomposite membranes were prepared using electrospinning technique and modified with TiO2 nanoparticles. Their photocatalytic activity towards dye degradation and regeneration tendency was investigated [24]. Surface imprinted chitosan-TiO2 composites (SICT) was prepared using methyl orange as template [25]. Recently, aerochitin-titania (TiO2) composite was synthesized, which shows excellent adsorptive and photocatalytic activity for degradation of the model organic pollutant, methylene blue (MB) dye, under UV irradiation [26].

To the best of our knowledge, no reports on the greener synthesis and application of chitosan/polyacrylic acid/TiO2 bionanocomposites in the area of visible light induced photocatalysis appeared in the literature. The aim of the present investigation is to assess the influence of modified amphoteric biopolymer chitosan on the performance of TiO2 photocatalyst, particularly in visible region. The present paper reports the greener synthesis of amphoteric chitosan/acrylic-TiO2 bionanocomposites using environmentally friendly ultrasound waves and their performance in white light induced photocatalytic degradation of industrial dye, malachite green.

2. Material and Methods

2.1. Chemicals

The following chemicals of analytical grade were used for synthesis of grafted CA/CAT bionanocomposite and photodegradation studies. Chitosan and acrylic acid used were purchased from Himedia, Loba Chemie. Malachite green was obtained from the Merck. Millipore water was used for preparing various solutions.

2.2. Ultrasonic Assisted Synthesis of Grafted Chitosan/TiO2 Bionanocomposites

Chitosan-acrylic acid biopolymer was synthesized by dissolving 0.5 g of chitosan in 10 ml acetic acid (3%) and left overnight for complete dissolution. The 15 ml of monomer acrylic acid (5 mol/L) was added dropwise to the viscous chitosan solution, followed by addition of 10 ml of initiator potassium persulfate (0.25mol/L) with continuous stirring. The reaction mixture was subjected to ultrasonic waves at 40 KHz in an ultrasonic bath for 30 min, till thick white solution was obtained. The product was transferred to the Petri dish and dried in oven for 3 days at 60°C. The gel formed was subsequently washed twice with lukewarm water to remove the monomer left and was confirmed by the pH measurements. The optimized conditions for better yield of the product was obtained by performing the polymerization reaction by varying the amount of monomer (10, 20, 30, 40 ml), amount of potassium persulfate (12, 14, 16 ml), and time period for the exposure of ultrasonic waves (15, 20, 30, 45 mins).

TiO2 nanoparticles were prepared by dissolving 8.52 gm of titanium isopropoxide in 20 mL ethanol followed by addition of 10% NH4OH with continuous stirring till complete precipitation occurred. The reaction mixture after half an hour vigorous stirring was subjected to sonication in ultrasonic bath for 40 minutes, further followed by stirring for an hour, and kept overnight. The yellow colored precipitates obtained were purified by washing with methanol and filtered. The resultant product was dried in an oven at 100°C for 2 hours and calcinated at 450°C [17].

In order to obtain the chitosan-acrylic acid based nanocomposites, 100 mg of TiO2 nanoparticles was dissolved to make suspension in iso-butyl alcohol, followed by ultrasonication for 1 hr to attain well dispersed solution. The resultant nanoparticles solution was added to the polymerization reaction mixture of chitosan-acrylic acid prepared under optimized reaction conditions as discussed in proceeding section, followed by continuous stirring for 2 hrs on magnetic stirrer. The reaction was proceeded further for 30 mins under ultrasonic waves, and the product obtained was transferred to the Petri dish and dried in oven for 3 days at 60°C.

2.3. Instruments Used for CAT Nanocomposite Characterization and Photocatalytic Studies

X’Pert Pro was used for obtaining XRD graph of CAT. It is equipped with X’Celerator solid-state detector, using Cu-Kα radiation (λ = 0.15418 nm). The sample was analyzed over 2ϴ collection range 20-800. The accelerating voltage of 40 kv, emission current of 30 milliampere, and the scanning speed of 4.4 counts per second were used. FE-SEM (Carl Zeiss, Merlin compact model) at an accelerating voltage of 20kV was used to obtain microscopic feature of nanocomposite coated on gold. FT-IR spectra were recorded on Bruker FT-IR spectrophotometer. UV-VIS spectrometer (Shimadzu UV-1800) was used for studying the photocatalytic degradation of malachite green. Thermal analysis up to 8000°C was done with the Shimadzu TGA-50 instrument. The photochemical experiments were performed in specially designed photocatalytic reactor equipped with white light source. An ultrasonicator of Labman Scientific instruments Pvt. Ltd. having a frequency of 40 KHz was used to impose sound waves for the synthesis of uniformly distributed metal oxide photocatalysts.

2.4. Photocatalytic Degradation Studies
2.4.1. Photocatalytic Degradation of Malachite Green Using CAT

A specially designed double walled reaction vessel (volume 250 ml) was manufactured to evaluate the photocatalytic activity. The reactor was outfitted with white LED bulbs. The photocatalytic degradation studies were conducted on synthetic dye, malachite green, and organophosphate pesticide, quinalphos. To 100 ml of 10 ppm malachite green, 100 mg of CAT was added and the resulting solution was kept for 30 min in dark. The absorbance was recorded. The solution was exposed to the white light (15W). The rate of degradation was studied by monitoring the changes in the UV-Vis absorption at λmax 617 nm. Degradation efficiency (%) has been calculated as follows.

3. Result and Discussion

Chitosan-acrylic acid/TiO2 bionanocomposite was synthesized using greener ultrasonication technique and the optimized conditions for better percentage yield of the product obtained were found to be 15ml acrylic acid, 10 ml K2S2O8, and reaction time 30 min. Further, the polymerization reaction was carried out under optimized conditions to obtain bionanocomposite CAT. Acrylic acid monomer was anchored at the chitosan backbone in the presence of potassium persulfate as initiator. The free radical mechanism proposed for synthesis of chitosan-acrylic acid is in accordance with the earlier one reported for radical polymerization [27]. The proposed mechanism for synthesis of CAT is as follows.

Step 1. The first step in the polymerization reaction involves the generation of the free radicals , HO.
Generation of Free Radical (, )

Step 2. The formation of acrylic acid free radical from vinyl monomer took place as it is susceptible to free radical attack. Simultaneously, free radical may also attack the chitosan at probable positions.
Chain Initiation
Probabilities

Step 3. The growing chains of the polymer get joined together and incorporate the TiO2 to form the desired nanocomposite. CA has pendant -COOH groups, along with terminal chain groups, i.e., primary and secondary -OH and -NH2, which provides the sites for TiO2 incorporation in the polymeric matrix. This is in accordance with the proposed mechanism for self-assembly between TiO2 nanoparticles and polymer with COOH groups [28].
Polymerization and Nanocomposite Formation

The synthesized CAT was characterized by physiochemical techniques such as X-ray diffraction (XRD), field emission scanning electron microscope (FE-SEM), Fourier Transform Infra-Red spectroscopy (FT-IR), Energy Dispersive X-ray spectroscopy (EDX), and Thermal Gravimetric Analysis (TGA) to obtain the surface morphology, elemental composition, and thermal analysis.

3.1. X-Ray Diffraction Studies

XRD patterns of TiO2, CA, and CAT are shown in Figures 1(a)1(c), respectively. The typical X-ray diffraction patterns of the synthesized TiO2 show strong diffraction peaks at 25.4°, 37.05°, 38.6°, 48.15°, 53.92°, and 75.28° and were matched with JCPDS card number 01-073-1764 [17]. X-ray studies support the formation of anatase phase as the main crystal phase for synthesized TiO2. In case of bionanocomposite, CAT sharp peaks at 25.4329, 28.8921, 39.5873, 48.3106, and 51.8367 were observed, which clearly reflects the incorporation of TiO2 into chitosan/acrylic grafted biopolymer.

3.2. FT-IR Analysis

FT-IR spectra of CA biopolymer (Figure 2(a)) show peak at 2924 cm−1 with broad band at 3000-3500 cm−1 which corresponds to NH2 and -OH group as compared to the pure chitosan [29]. The -C=O bond of carboxylic group of acrylic acid, giving intense peak at 1719 cm−1, confirms the grafting of acrylic acid onto chitosan, and the peak observed at 1263 cm−1 is due to bending vibrations of (C-O) group [29]. In CAT bionanocomposite (Figure 2(b)), there is decrease in intensity peaks at 2968 cm−1 which may be due to loss of double bond character of carbon and presence of -C=O group was evident from peak at 1714 cm−1. The additional peaks at 964 cm-1 and 809 cm-1 were due to the presence of Ti-O-C bond and Ti-O bond, respectively [30].

3.3. Surface Morphology Analysis

The surface morphology of CA and CAT was investigated by FE-SEM and images are given in Figures 3(a)-3(b), respectively. The morphologies of grafted polymer shows the incorporation of grafted chains of acrylic acid into the backbone. SEM image of CAT indicates the uniform incorporation of TiO2 nanoparticles into the grafted matrix owing to the strong interactions between amphoteric chitosan-acrylic acid and TiO2. Further, the modification of surface morphology is evident from the formation of spherical globules interlinked structure as compared with the cloudy morphology of acrylic acid grafted chitosan due to the transformation of inorganic/polymeric material into composite material with an interlinked structure. The winding of polymer chains around the TiO2 nanoparticles resulted in the growth of globular shaped network nanocomposites. Similar type of observations was reported for chitosan-ZnO/polyaniline hybrid composites and chitosan (CS) and cellulose acetate (CA) blends containing titanium dioxide (TiO2) nanoparticles [31, 32]. The elemental composition of CA and CAT was confirmed from EDX studies. The presence of TiO2 in the nanocomposite CAT is evident from EDX graph (Figures 4(a) and 4(b)).

3.4. Thermal Analysis

Thermal analysis curve corresponds to CAT bionanocomposite (Figure 5) showed well differentiation weight loss steps. The first step corresponds to loss of water molecule and any volatile components (4.09%) at 101.4°C. The initial decomposition occurring at temperature 252.2°C corresponds to 46.20% weight loss which may be due to breakage/dissociation of the grafted chains from backbone. The other decomposition peak was observed at 354.3°C and 505° due to partial dissociation of chitosan chains and due to the breakage of TiO2 molecules from back bone, and the mass left at 628°C corresponds to 11.126% TiO2 while in case of chitosan-acrylic acid grafted polymer, the final decomposition temperature was less (580°C) with 4.8% polymeric mass left [33].

4. Kinetics of Photocatalytic Degradation of Malachite Green under White Light Using CAT

Photocatalytic activity of the chitosan-acrylic acid/TiO2 nanocomposite was studied for the photocatalytic degradation of the malachite green dye under the white light. Malachite green shows the absorption peaks at 617 nm in visible region and 316 nm in the UV region. Photocatalytic degradation of malachite green dye has been studied under three different conditions: (i) under white light, (ii) synthesized TiO2 under white light, (iii) CAT bionanocomposites under white light (Figure 6). The result confirms that the highest degradation of the malachite green dye resulted in the presence of CAT under white light.

The time dependent UV-Vis spectra of malachite green were shown in Figure 7. The decrease in the intensity of both the peaks has been observed with time. Further the degradation of dye during exposure to white light was reflected from the diminishing of the peaks in UV-Vis region. It has been found that 91.94% of dye has been degraded with CAT.

The pH of the solution plays an important role in the photocatalytic degradation of dye; therefore experiments were performed with 100 ml (10ppm of MG) by varying pH of the solution from 2 to 10 keeping the dose of CAT (100mg) constant. It has been observed that maximum degradation was observed at pH 7 (91.94%) followed by 52.46, 60.7, and 58.2% at pH value of 10, 4, and 2, respectively (Figure 8).

Photocatalytic experiments for degradation of malachite green were also performed by changing the initial concentration from 5 to 50 ppm. It has been observed that as the concentration of dye increased, the rate of photocatalytic degradation decreases. Figure 9 showed that for 5 ppm, 10 ppm, 25 ppm, and 50 ppm solution of malachite green, degradation obtained was 99.5%, 91.94%, 58.01, and 38.92%, respectively. For 10 ppm of the malachite green solution, degradation was 91.94% in 240 min.

The rate of degradation of the malachite green (10 ppm) is shown in Figure 10. The experimental data was fit into the Langmuir-Hinshelwood equation, ln (C0/) = kt, where C0 is initial concentration and is concentration at time t. The rate constant for the degradation of the malachite green was found to be 7.13x10−3 min−1.

The plausible explanation for the performance of bionanocomposites as photocatalyst in white light is as follows:

(i) Synthesized bionanocomposite successfully improves the efficiency of the well-known photocatalyst TiO2 for degradation of the commercial dye malachite green by preventing the recombination reaction. It may be attributed to efficient charge separation of the electrons and holes at the interface of polymer/TiO2 nanocomposites [34].

(ii) Improvement in photocatalytic efficiency observed with CA/TiO2 nanocomposites may be attributed to polymeric backbone which provides the number of functional groups for adsorption of pollutants in proximity of the catalyst.

(iii) As the usage of TiO2 in suspension mode needs liquid-solid separation, the bionanocomposite solves the problem of the recovery and reusability of photocatalyst.

(iv) The most important observation in the present investigation is the response of photocatalytic degradation by absorption of visible light; otherwise, TiO2 has absorption edge is in UV region. This probably can be explained as follows: binding of TiO2 to the amphoteric chitosan resulted in mixing of the metal orbitals with the ligand orbitals or extension of conjugation which allows the movement of electrons in the extended space and leads to the lowering of the excitation energy. This may lead to the response of photocatalyst embedded in nanocomposites in the visible light. Moreover, the presence of n &  π system of the CAT provided further movement of the electron, thereby preventing recombination reaction.

5. Conclusions

The greener synthesis CA/TiO2 nanocomposites were synthesized from grafted acrylic acid/chitosan which contains a weak anionic group (-COOH) using ultrasonic waves. The synthesized CA (acrylic acid/chitosan) and CAT (CA/TiO2) were characterized by employing various physiochemical techniques such as FT-IR spectroscopy, XRD, thermal analysis, morphological analysis, and EDX. The photocatalytic efficiency of CAT in white light was investigated for degradation of industrial dye-malachite green. The rate constant of the reaction for degradation of malachite green was found to be 7.13x10−3 min−1. The development of novel polymeric nanocomposites offers the potential to introduce new traits in the waste water treatment technology. The response of nanocomposites in the visible light is much desired characteristics for finding an energy and cost-effective solutions for photocatalysis based water purification and treatment.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.

Disclosure

The abstract was presented in the 4th Edition of International Conference on Polymer Science and Technology.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

The authors are thankful to the authorities of Sant Longowal Institute of Engineering and Technology, Longowal, for providing financial assistance. They are also pleased to acknowledge the facilities provided by Panjab University, Chandigarh; All India Institutes of Medical Sciences (AIIMS), Delhi; Central University, Bathinda; National Institute of Technology, Jalandhar; and Thapar University, Patiala.

References

  1. M. W. Luckenbach, P. D. Fur, M. L. Kellogg, and P. V. Veld, “Potential effects of endocrine disrupting compounds on bivalve populations in chesapeake bay: a review of current knowledge and assessment of research needs,” in Chesapeake Research Consortium, pp. 10–170, Edgewater, NJ, USA, 2009. View at: Google Scholar
  2. H. D. Mansilla, M. C. Cristina Yeber, J. Freer, J. Rodríguez, and J. Baeza, “Homogeneous and heterogeneous advanced oxidation of a bleaching effluent from the pulp and paper industry,” Water Science and Technology, vol. 35, no. 4, pp. 273–278, 1997. View at: Publisher Site | Google Scholar
  3. C. M. Browner, J. C. Fox, S. Frace, M. B. Rubin, E. B. Chief, and F. Hund, Development document for final effluent limitations guidelines and standards for the pharmaceutical manufacturing point source category, Engineering and Analysis Division Office Science and Technology, US Environmental Protection Agency, Wash, USA, 1998.
  4. M. Noorjahan, M. Pratap Reddy, V. Durga Kumari, B. Lavédrine, P. Boule, and M. Subrahmanyam, “Photocatalytic degradation of H-acid over a novel TiO2 thin film fixed bed reactor and in aqueous suspensions,” Journal of Photochemistry and Photobiology A: Chemistry, vol. 156, no. 1-3, pp. 179–187, 2003. View at: Publisher Site | Google Scholar
  5. I. M. Arabatzis, S. Antonaraki, T. Stergiopoulos et al., “Preparation, characterization and photocatalytic activity of nanocrystalline thin film TiO2 catalysts towards 3,5-dichlorophenol degradation,” Journal of Photochemistry and Photobiology A: Chemistry, vol. 149, no. 1–3, pp. 237–245, 2002. View at: Publisher Site | Google Scholar
  6. F. Kiriakidou, D. I. Kondarides, and X. E. Verykios, “The effect of operational parameters and TiO2-doping on the photocatalytic degradation of azo-dyes,” Catalysis Today, vol. 54, no. 1, pp. 119–130, 1999. View at: Publisher Site | Google Scholar
  7. Y. Hu, H. Tsai, and C. Huang, “Effect of brookite phase on the anatase–rutile transition in titania nanoparticles,” Journal of the European Ceramic Society, vol. 23, no. 5, pp. 691–696, 2003. View at: Publisher Site | Google Scholar
  8. J. Fisher and T. A. Egerton, Titanium compounds , inorganic, Kirk-Othmer encyclopaedia of chemical technology, Wiley, New York, NY, USA, 2001.
  9. A. Di Paola, E. García-López, S. Ikeda, G. Marc, B. Ohtani, and L. Palmisano, “Photocatalytic degradation of organic compounds in aqueous systems by transition metal doped polycrystalline TiO2,” Catalysis Today, vol. 75, no. 1–4, pp. 87–93, 2002. View at: Publisher Site | Google Scholar
  10. M. R. Hoffmann, S. T. Martin, W. Y. Choi, and D. W. Bahnemann, “Environmental applications of semiconductor photocatalysis,” Chemical Reviews, vol. 95, no. 1, pp. 69–96, 1995. View at: Publisher Site | Google Scholar
  11. E. Bet-Moushoul, Y. Mansourpanah, K. Farhadi, and M. Tabatabaei, “TiO2 nanocomposite based polymeric membranes: a review on performance improvement for various applications in chemical engineering processes,” Chemical Engineering Journal, vol. 283, pp. 29–46, 2016. View at: Publisher Site | Google Scholar
  12. R. Asahi, T. Morikawa, T. Ohwaki, K. Aoki, and Y. Taga, “Visible-light photocatalysis in nitrogen-doped titanium oxides,” Science, vol. 293, no. 5528, pp. 269–271, 2001. View at: Publisher Site | Google Scholar
  13. L. Jianhua, Y. Rong, and L. Songmei, “Preparation and characterization of the TiO2-V2O5 photocatalyst with visible-light activity,” Rare Metals, vol. 25, pp. 636–642, 2006. View at: Google Scholar
  14. P. Kaur and D. Sud, “Photocatalytic degradation of quinalphos in aqueous TiO2 suspension: Reaction pathway and identification of intermediates by GC/MS,” Journal of Molecular Catalysis A: Chemical, vol. 365, pp. 32–38, 2012. View at: Publisher Site | Google Scholar
  15. F. Peng, L. Cai, L. Huang, H. Yu, and H. Wang, “Preparation of nitrogen-doped titanium dioxide with visible-light photocatalytic activity using a facile hydrothermal method,” Journal of Physics and Chemistry of Solids, vol. 69, no. 7, pp. 1657–1664, 2008. View at: Publisher Site | Google Scholar
  16. I. Nakamura, N. Negishi, S. Kutsuna, T. Ihara, S. Sugihara, and K. Takeuchi, “Role of oxygen vacancy in the plasma-treated TiO2 photocatalyst with visible light activity for NO removal,” Journal of Molecular Catalysis A: Chemical, vol. 161, no. 1-2, pp. 205–212, 2000. View at: Publisher Site | Google Scholar
  17. N. Sharotri and D. Sud, “Greener approach to synthesize visible light responsive nanoporous S-doped TiO2with enhanced photocatalytic activity,” New Journal of Chemistry, vol. 39, no. 3, pp. 2217–2223, 2015. View at: Publisher Site | Google Scholar
  18. N. Sharotri and D. Sud, “Studies on visible light induced photocatalysis by synthesized novel Mn-S co-doped TiO2 for remediation of pollutants. Sep puriftechnol,” Separation and Purification Technology, vol. 183, pp. 382–391, 2017. View at: Publisher Site | Google Scholar
  19. M. De Lima, M. Freire, J. Fonseca, and M. Pereira, “Chitosan membranes modified by contact with poly(acrylic acid),” Carbohydrate Research, vol. 344, no. 13, pp. 1709–1715, 2009. View at: Publisher Site | Google Scholar
  20. S. Benamer, M. Mahlous, D. Tahtat et al., “Radiation synthesis of chitosan beads grafted with acrylic acid for metal ions sorption,” Radiation Physics and Chemistry, vol. 80, no. 12, pp. 1391–1397, 2011. View at: Publisher Site | Google Scholar
  21. Y. Wu, J. Guo, W. Yang, C. Wang, and S. Fu, “Preparation and characterization of chitosan–poly(acrylic acid) polymer magnetic microspheres,” Polymer Journal, vol. 47, no. 15, pp. 5287–5294, 2006. View at: Publisher Site | Google Scholar
  22. Y.-E. Moon, G. Jung, J. Yun, and H.-I. Kim, “Poly(vinyl alcohol)/poly(acrylic acid)/TiO2/graphene oxide nanocomposite hydrogels for pH-sensitive photocatalytic degradation of organic pollutants,” Materials Science and Engineering: B Advanced Functional Solid-State Materials, vol. 178, no. 17, pp. 1097–1103, 2013. View at: Publisher Site | Google Scholar
  23. C. Hou, T. Jiao, R. Xing, Y. Chen, J. Zhou, and L. Zhang, “Preparation of TiO2 nanoparticles modified electrospun nanocomposite membranes toward efficient dye degradation for wastewater treatment,” Journal of the Taiwan Institute of Chemical Engineers, vol. 78, pp. 118–126, 2017. View at: Publisher Site | Google Scholar
  24. G. Xiao, H. Su, and T. Tan, “Synthesis of core–shell bioaffinity chitosan–TiO2composite and its environmental applications,” Journal of Hazardous Materials, vol. 283, pp. 888–896, 2015. View at: Publisher Site | Google Scholar
  25. A. Pawlak and M. Mucha, “Thermogravimetric and FTIR studies of chitosan blends,” Thermochimica Acta, vol. 396, no. 1-2, pp. 153–166, 2003. View at: Publisher Site | Google Scholar
  26. R. S. Dassanayake, E. Rajakaruna, and N. Abidi, “Preparation of aerochitin TiO2 composite for efficient photocatalytic degradation of methylene blue,” Journal of Applied Polymer Science, vol. 135, no. 8, p. 45908, 2017. View at: Publisher Site | Google Scholar
  27. BS. Saruchi Kaith, R. Jindal, and G. Kapur, “Enzyme-based green approach for the synthesis of gum tragacanth and acrylic acid cross-linked hydrogel: its utilization in controlled fertilizer release and enhancement of water-holding capacity of soil,” Iranian Polymer Journal, vol. 22, pp. 561–570, 2013. View at: Google Scholar
  28. M. Luo, W. Tang, J. Zhao, and C. Pu, “Hydrophilic modification of poly(ether sulfone) used TiO2 nanoparticles by a sol–gel process,” Journal of Materials Processing Technology, vol. 172, no. 3, pp. 431–436, 2006. View at: Publisher Site | Google Scholar
  29. P. Kannusamy and T. Sivalingam, “Chitosan-ZnO/polyaniline hybrid composites: polymerization of aniline with chitosan-ZnO for better thermal and electrical property,” Polymer Degradation and Stability, vol. 98, no. 5, pp. 988–996, 2013. View at: Publisher Site | Google Scholar
  30. G. Lui, J.-Y. Liao, A. Duan, Z. Zhang, M. Fowler, and A. Yu, “Graphene-wrapped hierarchical TiO2 nanoflower composites with enhanced photocatalytic performance,” Journal of Materials Chemistry A, vol. 1, no. 39, pp. 12255–12262, 2013. View at: Publisher Site | Google Scholar
  31. S. H. Kim, S.-Y. Kwak, B.-H. Sohn, and T. H. Park, “Design of TiO2 nanoparticle self-assembled aromatic polyamide thin-film-composite (TFC) membrane as an approach to solve biofouling problem,” Journal of Membrane Science, vol. 211, no. 1, pp. 157–165, 2003. View at: Publisher Site | Google Scholar
  32. S. Mafirad, M. R. Mehrnia, P. Zahedi, and S. Hosseini, “Chitosan-based nanocomposite membranes with improved properties: effect of cellulose acetate blending and TiO2 nanoparticles incorporation,” Polymer Composites, vol. 39, no. 12, pp. 4452–4466, 2017. View at: Publisher Site | Google Scholar
  33. N. Bhullar, K. Kumari, and D. Sud, “Studies on chitosan-based superhydrophilic adsorbent for phasing out Rhodamine 6G dye and Cd2+ ions from aqueous solutions,” Desalination and Water Treatment, vol. 95, pp. 355–364, 2017. View at: Publisher Site | Google Scholar
  34. S. Ameen, M. S. Akhtar, Y. S. Kim, and H. S. Shin, “Nanocomposites of poly(1- naphthylamine)/SiO2 and poly(1-naphthylamine)/TiO2: comparative photocatalytic activity evaluation towards methylene blue dye,” Applied Catalysis B: Environmental, vol. 103, no. 1-2, pp. 136–142, 2011. View at: Publisher Site | Google Scholar

Copyright © 2019 M. Bahal et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.


More related articles

812 Views | 376 Downloads | 2 Citations
 PDF  Download Citation  Citation
 Download other formatsMore
 Order printed copiesOrder

Related articles

We are committed to sharing findings related to COVID-19 as quickly and safely as possible. Any author submitting a COVID-19 paper should notify us at help@hindawi.com to ensure their research is fast-tracked and made available on a preprint server as soon as possible. We will be providing unlimited waivers of publication charges for accepted articles related to COVID-19. Sign up here as a reviewer to help fast-track new submissions.