The present thesis is focused on the synthesis and environmental applications of polyaniline and its nanocomposites. It is organized in six chapters and brief discussions of the contents of the individual chapters are given below. Chapter 1 reviews two important water purification methods: adsorption and photocatalysis, which are widely discussed in literature. A general introduction to conducting polymers has been given and their photocatalytic activity has been described. Chapter 2 reports the application of polyaniline emeraldine salt for the removal of anionic dyes from aqueous solutions by adsorption. A possible mechanism for the anionic dye adsorption by PANI emeraldine salt has been proposed. The electrostatic interaction between the positively charged PANI backbone and dye anions is responsible for significant dye adsorption. The kinetic parameters for the adsorption of anionic dyes on PANI have also been determined. In Chapter 3, we investigate the adsorption and desorption of anionic dyes from aqueous solution by PANI doped with different protonic acids. PANI with three dopants, namely p-toluene sulfonic acid (PTSA), camphor sulfonic acid (CSA) and dodecyl benzene sulfonic acid (DBSA) were used to adsorb various dyes. The adsorbed dyes were desorbed from the polymer by using a basic aqueous solution. It was found that the adsorption of dye is dependent on the size and nature of the dopant acids. The influence of different dopants on the adsorption and desorption kinetic parameters was also examined. In chapter 4, the inherent property of PANI to adsorb dyes has been explored for the detection of dyes by electrochemical method. The changes in the CV of PANI film coated on Pt electrodes on addition of dye have been employed for detection of dye in aqueous solution. Furthermore, PANI coated stainless steel (SS) electrodes show a change in current intensity of Fe2+/Fe3+ redox peaks due to addition of dye in the electrolyte solution. Chapter 5 describes the synthesis and characterization of polyaniline-grafted-chitosan (CPANI) with different grafting ratios. The mechanical properties and the crystallinity of CPANI were investigated by means of nanoindentation and X-ray diffraction experiments, respectively. CPANI has been further self-assembled into multilayer thin film via versatile and simple layer-by-layer (LbL) approach. Negatively charged hyaluronic acid (HUA) was used as complementary polyelectrolyte for the self-assembly. LbL growth of the multilayer thin films has been monitored with UV-vis spectral analysis as well as by AFM. The formation of thin film has been further characterized by SEM. The pH responsive behavior of CPANI/HUA multilayer thin film has been investigated. Reusability of this thin film has been investigated by repeating the pH responsive experiments for 10 cycles. Chapter 6 is focused on the preparation of nanocomposite thin films of CPANI/PSS/TiO2 via LbL approach. LbL growth of this self-assembly was monitored by UV-vis spectral analysis and porous nature was observed from SEM images. Poly (styrene sulfonate) (PSS) was used as bridging layer between TiO2 nanoparticles and CPANI for the multilayer self-assembly. Incorporation of CPANI within this LbL self-assembly enhanced the dye degradation ability of the thin film by increasing the availability of dye molecules around the TiO2 nanoparticles. Furthermore, CPANI may act as a sensitizer to enhance the photocatalytic activity of TiO2. The effects of surface area of the multilayer thin film and amount of catalysts (TiO2 nanoparticles) incorporated in the self-assembly were described based on the kinetics of the dye degradation reactions. The same multilayer thin film can be efficiently used for dye degradation several times. The work presented in this thesis utilizes unique dye adsorption properties of PANI and its copolymers. The change in conductivity of PANI after dye adsorption and the electrochemical dye detection in aqueous medium promise the potential of PANI as a dye sensing material in waste water at very low concentration. The nanocomposites of CPANI/PSS/TiO2 present a novel material for photocatalysis.

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M. Tech. (Department of Chemical Engineering, Faculty of Engineering and Technology), Vaal University of Technology. / This work investigates the possible use of chitosan beads and polyaniline grafted chitosan beads (PGCB) for the adsorption of copper ions from copper contaminated water. For this purpose chitosan flakes were converted to chitosan beads. However, a variable from a number of reaction variables (aniline concentration, chitosan concentration, temperature, acid concentration, reaction time and initiator concentration) was varied while others was kept constant, in an attempt to determine the best conditions for grafting of polyaniline onto chitosan beads. Percentage (%) grafting and % efficiency were key parameters used to determine such conditions. The chitosan beads and PGCB were characterized using physical techniques such as Fourier transformed infra red (FTIR), X-ray diffraction (XRD), and scanning electron microscope (SEM). The beads were used as an adsorbent for copper ions removal. The effect of pH on the removal rate of copper (II) by PGCB was investigated on by varying the pH values from pH 3 to 8 at an initial concentration of 40 mg/l. The effect of contact time, initial concentration and temperature was also investigated. The Langmuir and Freundlich model were used to describe adsorption isotherms for chitosan beads and PGCB, with correlation coefficient (R2) as the determining factor of best fit model. The thermodynamics of adsorption of copper (II) onto PGCB was described by parameters such as standard Gibb’s free energy change (ΔGo), standard enthalpy change (ΔHo), and standard entropy change (ΔSo) while the pseudo first-order and pseudo second-order kinetic model was used to describe kinetic data for the PGCB, with R2 and chi- square test (  2) as the determinant factor of best fit model. From the desorption studies, the effect of eluants (HCl and HNO3) and contact time on percentage desorption of PGCB loaded copper (II) ion was investigated upon. In determining the reusability of the PGCB loaded copper (II) ion, three cycles of adsorption/desorption studies was carried out. The results obtained from determining the best conditions for grafting polyaniline onto chitosan beads revealed the following grafting conditions; [Aniline] 0.1 g/l, [temperature] 35oC, [chitosan] 0.45 g/l, [HCl] 0.4 g/l, [(NH4)2S2O8] 0.35 g/l, and [time] 1 h. These conditions were applied in the grafting of polyaniline onto chitosan beads. FTIR analysis showed increase intensity in the grafted beads which provided evidence of grafting, XRD measurement showed a decrease in crystallinity in the PGCB as against the partial crystalline nature of chitosan. In SEM analysis, evidence of grafting was revealed by the closed gap between the polysaccharide particles in the PGCB. From the investigation carried out on the effect of pH on the percentage removal of Cu(II) ions by PGCB, the optimal pH value was found to be pH 5 with a percentage removal of 100% and this value was used for all adsorption experiment. Also from the investigation performed on the effect of contact time and initial concentration, it was observed that there was a sharp increase in the amount of Cu(II) ions adsorbed by PGCB up until contact time of 30 min and thereafter, it increases gradually. From the experiment carried out on the effect of temperature on adsorption capacity, there was an increase in adsorption capacity with increase in temperature. Moreover, at temperatures of 25oC, 35 oC and 45oC the Langmuir model gave the best fit for the chitosan beads having R2 values that are equal and greater than 0.942 in contrast to Freundlich having R2 values that is equal and greater than 0.932. The maximum adsorption capacity (Qm) from Langmuir model at these temperatures were 30.3 mg/g, 47.6 mg/g and 52.6 mg/g respectively. Also, the Langmuir model gave the best fit for the PGCB having R2 values that are equal and greater than 0.956 in contrast to Freundlich model with R2 values that is equal and greater than 0.935. The Qm from Langmuir model at these temperatures were 80.3 mg/g, 90.9 mg/g and 100 mg/g respectively. The values of Qm for PGCB appears to be significantly higher when compared to that of chitosan beads and this makes PGCB a better adsorbent than chitosan beads. From the thermodynamic studies carried out on PGCB, the values of ΔGo were negative and this denotes that the adsorption of copper ions onto PGCB is favorable and spontaneous, the positive value of ΔHo shows the adsorption process is endothermic and the positive value of ΔSo illustrate increased randomness at the solid-liquid interface during the adsorption process. Also, from the kinetic studies carried out on the PGCB, the pseudo second-order kinetic model best described the kinetic data having R2 values that are equal and greater than 0.994 in contrast to the pseudo first-order kinetic model with R2 values that is equal and greater than 0.913. The  2 values for the pseudo first-order and pseudo second-order kinetic model were similar; however, there was a large difference for qe between the calculated (qeCal) values of the first-order kinetic model and experimental (qeExp) values. In the case of the pseudo second-order model, the calculated qe values agree very well with the experimental data. Desorption of the metal ions from PGCB was efficient. 0.5 M HCl was successfully used in desorbing the beads loaded with copper ions and a percentage desorption of 97.1% was achieved at contact time of 180 min. PGCB were successfully re-used for adsorption/desorption studies were a Qm of 83.3 mg/g, 83.3 mg/g and 76.9 mg/g was achieved in the first, second and third cycle respectively.

To produce a greener adhesive is always an issue of concern to the commercial market and global environment. The environmental request for producing greener and bio-based adhesives leads to an increased awareness of replacing fossil-based components in adhesives with bio-based alternatives. Consequently, many researchers try to graft polymers from natural materials and some achievements have been made. In this work, an improved procedure to graft vinyl acetate (VAc) from chitosan (CS) is proposed and significant improvements were made regarding the increased Tg and water resistance. The achieved monomer conversion of VAc was ~97 %, and it was confirmed that chitosan-graft-poly(vinyl acetate) (CS-g-PVAc) could be used as a wood adhesive. The adhesive exhibited competitive properties to commercial PVAc wood adhesive. In the produced CS-g-PVAc, ~17 % of the fossil-based content of VAc could be replaced with bio-based chitosan, indicating an increased sustainability. At the same time there is no residual monomer during pressing, which avoid to pollute environment and hurt human. Compared to commercial PVAc, which has Tg at ~28 ℃, the Tg of CS-g-PVAc is ~42 ℃ At the same time, the water resistance of PVAc adhesive was successfully increased.