ELECTROCHEMICAL DETECTION OF HYDROQUINONE USING GLASSY CARBON ELECTRODE MODIFIED WITH POLYANILINE DECORATED WITH NITROGEN DOPED GRAPHENE OXIDE By Allen Sedze (R133434V) Submitted in partial fulfilment of the requirements for the degree of Bachelor of Science Honours in Chemical Technology Department of Chemical Technology in the Faculty of Science and Technology at the Midlands State University Supervisor: Professor Mambo Moyo May 2017 DEDICATION This project is dedicated to my loving parents Mr. and Mrs. Sedze for their unconditional and lasting love and prayers. I express my sincere gratitude to them and my loving sister Martha T. and brother Tendai D. Thank you so much for your unwavering support. 1 ACKNOWLEDGEMENTS First and foremost, I offer my sincerest gratitude to the Almighty God. I give Him all the glory, honour and adoration for seeing me through this journey, giving the strength and wisdom through the Holy Spirit and letting me know that it is never too late to get a degree. I owe my deepest and immense gratitude to my supervisor Professor .M. Moyo whom God has blessed me with and has chosen to be my supervisor, mentor and instructor, for his unwavering guidance throughout the journey and making me to believe in myself that I can do it. I will forever be grateful for your kindness. Goethe said, “Treat people as if they were what they ought to be and you help them to become what they are capable of being.” You have treated me as though I were capable of reaching the stars. Because of you, I have. ‘You are Awesome indeed’. To my friends, colleagues and loved ones in the Lab cascading from top to bottom Mrs. M. Gonzo down to Fuyana Vezubuhle and other lab technician students, you are all gratefully acknowledged. All members of the Chemistry Department, Midlands State University, I say thank you for your cordial working relationship. Thank you, Lord Jesus. 2 ABSTRACT A simple sensitive low-cost electrochemical sensor for the detection and quantitative determination of hydroquinone. Nitrogen doped graphene oxide decorated with Polyaniline (NGO/PANI) was synthesized by a chemical method, then casted on a surface of glassy carbon electrode to form NGO/PANI-GCE. Electrochemical impedance spectroscopy and Bode plots were used to characterize the synthesized modifiers, NGO NPs, PANI NPs, NGO / PANI NPs and to probe the chemical linkage between NGO and PANI. Cyclic voltammetry, linear sweep, chronoamperometry and differential pulse voltammetry where used to assess the electro catalytic efficiency of the nanocomposite electrode towards the oxidation of hydroquinone. The electrode surface area after modification was 0.13 cm2, almost twice as large that of the bare glassy carbon electrode, indicating that the modified electrode displayed an improved surface area for electro catalysis. The modified electrode had a surface coverage of 1.31 x 10 constant, k was 3.9 x 10 6 M -1 -12 mol cm-2. The rate s-1, fast electron transfer during oxidation. The limit of detection for hydroquinone was 1.03569 x 10-7 M and the limit of quantification was 3.4531 x 10-7 M. The electrode exhibited good reproducibility with lower oxidation potential at 0.8 V and high sensitivity towards hydroquinone. 3 DECLARATION I, Allen Sedze., hereby declare that I am the sole author of this dissertation. I authorize Midlands State University to lend this dissertation to other institutions or individuals for the purpose of scholarly research. Signature ……………………………… Date …………………………………. 4 APPROVAL This dissertation entitled “Electrochemical detection uof hydroquinone using glassy carbon electrode modified with polyaniline decorated with nitrogen doped graphene oxide” by Allen Sedze meets the regulations governing the award of the degree of Chemical Technology of the Midlands State University, and is approved for its contribution to knowledge and literal presentation. Supervisor ……………………………………… Date ……………………………………………. 5 Table of Contents DEDICATION i ACKNOWLEDGEMENTS ii ABSTRACT iii DECLARATION iv APPROVAL v Chapter 1 0 1.0 Introduction 0 1.1 Background 0 1.2 Aims of the Research 2 1.3 Objectives 2 1.4 Problem Statement 3 1.5 Justification 4 CHAPTER 2 6 LITERATURE REVIEW 6 2.0 Summary 6 2.1 Hydroquinone 6 2.12 Reduction-oxidation equilibria 7 Graphene Oxide (GO) 7 2.1.2 Graphene oxide preparation using modified Hummer’s method 9 6 2.1.4 Properties of Graphene oxide 10 2.1.5 Chemical reactivity of graphene oxide 10 2.1.6 Nitrogen doped Graphene oxide 10 2.2 Polyaniline 11 2.2.1 Structure and oxidation state of Polyaniline 12 2.2.2 Conductivity in polyaniline 13 2.2.3 Synthesis of polyaniline 13 2.2.4 Doping in polyaniline 14 2.2.5 Polymer nanocomposites 14 2.2.6 Methods of preparation of polymer nanocomposite 15 2.2.7 Amalgamation/ Solution Mixing of Nitrogen doped graphene oxide and Polyaniline 15 2.3 Electrochemical Synergism 15 2.3.1 Electrode Modification 16 2.3.2 Characterisation of synthesized composite 17 Infrared spectroscopy, IR 17 Electrochemistry 18 2.4 Voltammetry 19 2.4.1 Instrumentation 19 2.4.2 The potentiostat 19 2.4.3 Electrodes 20 7 2.4.4 The reference electrode (RE) 20 2.4.5 Counter electrode (CE) 20 2.4.6 Working electrode (WE) 21 2.4.7 Cyclic voltammetry 21 2.4.8 Illustration of a typical cyclic sweep voltammetry. 21 Differential Pulse Voltammetry 25 Linear sweep voltammetry 25 Chronoamperometry 26 Electrochemical impedance spectroscopy 27 Bode Plots 27 2.5 Electro-catalysis 27 2.5.1 Chemically modified electrode 29 CHAPTER 3 31 EXPERIMENTAL 31 Introduction 31 3.1 Equipment 31 3.2 Chemicals and reagents 32 3.2.1 Synthesis procedures 32 Synthesis of Polyaniline 32 Synthesis of Polyaniline nanoparticles 33 8 3.2.2 Graphene oxide 33 3.2.3 Doping Nitrogen on Graphene oxide and modification with polyaniline 35 3.3 Characterization of the chemical modifiers and the composite 35 3.3.1 Fourier Transfer Infrared Spectroscopy (FTIR) 35 3.3.2 UV -Vis Spectroscopy 36 3.3.3 Electrode modification 36 3.4 Hydroquinone analysis 36 3.5 Electrochemical characterization 37 3.5.1 Electrochemical behavior of modifiers in 1 mM [Fe (CN)36]3-/4 solution 37 3.5.2 Electrochemical impedance spectroscopy and bode plots 37 3.5.3 Scan rate studies in in 1mM [Fe (CN)6]3-/4 solution 37 3.6 Optimisation of parameters 37 3.6.1 Effect of pH 37 3.6.2 Comparative studies in pH 4 phosphate buffer solution 38 3.6.3 Scan rate studies in pH 4 phosphate buffer solution 38 3.7 Kinetic studies 38 3.8 Langmuir adsorption isotherm studies 38 3.9 Catalytic rate constant 39 3.10 Differential pulse voltammetry 39 3.11 Stability studies 40 9 3.12 Reproducibility studies 40 Effect of interference 40 CHAPTER 4 41 RESULTS AND DISCUSSION 41 Introduction 41 4.1 NGO / PANI Np FTIR 42 4.2 Electrochemical characterisations 45 Voltammetric studies in 1.0 mM [Fe (CN)6]3-/4- in 1M KCl 45 4.3 Electrochemical impedance spectroscopy 47 Bode plots in 1.0 mM Fe(CN)6 3–/4– aqueous solution using 0.1 M KCl as the supporting electrolyte. 50 4.4 Surface area determination 51 4.5 Optimization of parameters 53 4.5.1 Effect of pH 53 4.6 Comparative study in pH 4 buffer 54 4.7 Scan rate studies in pH 4 phosphate buffer solution without an analyte 55 4.8 Comparative study in 1 mM hydroquinone in pH 4 PBS 4 55 4.9 Electrochemical impedance Spectroscopy in 1 mM Hydroquinone in pH 4 PBS 58 4.10 Bode Plots in 1mM hydroquinone 59 4.11 Kinetic studies of hydroquinone 60 10 Tafel slopes 61 Mechanism of hydroquinone oxidation with NGO / PANI-GCE 62 Linear Sweep Studies 64 Langmuir adsorption isotherm plot for NGO/PANI-GCE 65 4.16 Chronoamperometric Studies 66 Chronoamperograms for different Hydroquinone concentrations 67 Plots of 𝐼𝑐𝑎𝑡𝐼𝑏𝑢𝑓 vs. time 68 Plot of slopes2 vs. [Hydroquinone] 68 DPV for NGO/PANI -GCE 70 Stability 71 Reproducibility 72 Interference Studies 72 CHAPTER 5 73 5.0 Introduction 73 5.1 Conclusion 74 5,2 Recommendations 74 References 75 APPENDICES 85 APPENDIX A: MATERIALS 85 List A: Apparatus used in synthesis and characterisation 85 11 Table A1; Reagents and chemicals 85 Table A2 : Instrumentation 86 Treatment of Glassware 86 APPENDIX B: Working electrodes 87 B1: Working electrodes used in this study 87 APPENDIX C: Calculation 87 C1: Effective Surface area 87 Limit of Detection and Limit of Quantification 88 Excel Linest function 88 ABBREVIATIONS 12 EIS - Electrochemical impedance spectroscopy CA- Chronoamperometry CV- cyclic voltammetry NGO NPs – Nitrogen doped Graphene oxide nanoparticles PANI NPs – Polyaniline nanoparticles NGO/ PANI NPs– Nitrogen doped graphene oxide modified with polyaniline nanoparticles NGO-GCE – Nitrogen doped graphene oxide glassy carbon electrode PANI-GCE – Polyaniline modified glassy carbon electrode NGO/PANI-GCE – Glassy carbon electrode modified with Polyaniline decorated with nitrogen doped graphene oxide DPV- Differential pulse voltammetry DMSO- dimethylsulphoxide FTIR- Fourier Transfer Infrared GCE- Glassy carbon electrode LSV- Linear sweep voltammetry LOD- Limit of detection LOQ- Limit of quantification ICP – Intrinsically conducting polymer PANI NP s- polyaniline LIST OF FIGURES 13 FIG 1: CHEMICAL STRUCTURE OF HYDROQUINONE…………………………………………….1 Fig 2.1: Figure Schematic diagram of structure of graphene oxide (GO)………………………...8 Fig 2.3: GO synthesis ……………………………………………………………………………..9 Fig 2.3: GO synthesis ……………………………………………………………………………12 FIG 2.4 TYPICAL FT-IR SPECTRA OF GRAPHENE OXIDE……………………………………..18 Typical cyclic voltammogram for a reversible reaction………………………………………..24 Fig 3.1 Mechanism of polymerization of aniline monomer to polyaniline……………………..33 Fig 3.1: Synthesis of graphene oxide nanoparticles……………………………………………34 Fig 4.1 FT-IR Spectrum of (a) GO , (b) , PANI , (c) NGO- PANI Nps………………………41 Fig 4.1 FT-IR Spectrum of (a) GO , (b) , PANI , (c) NGO- PANI Nps………………………42 Fig 4.1.3 Polyaniline FTIR……………………………………………………………………43 Fig 4.1.3 UV- visible spectra of graphene oxide……………………………………………..44 Figure 4.1.4 Pani UV-Vis……………………………………………………………………44 Fig 4.2: Cyclic voltammograms for: a) bare GCE b) NGO- GCE c) PANIi-GCE d) NGO/PANIGCE in 1 mM [Fe (CN)6]3-/4- solution. Scan rate = 100 mV/s……………………………..45 Fig 4.3 Nyquist plots obtained for a) bare GCE b) NGO-GCE c) PANI -GCE d) and e) NGO/PANI -GCE in 1mM [Fe(CN)6] solution in 1M of KCl. Inset is the Randles circuit model used in fitting data……………………………………………………………………………….46 14 Fig 4.4 Bode (phase angle versus log f) plots obtained for i) bare GCE ii) NGO-GCE iii) PANI -GCE iv) and v) NGO/PANI -GCE in 1mM [Fe(CN)6] solution in 1M of KCl ………………..50 Fig 4.3 Effect of scan rate on peak potentials and currents (a) 50 mV/s, (b) 100 mV/s, (c) 150 mV/s, (d) 200 mV/s, (e) 250 mV/s, (f) 300 mV/s, (g) 350 mV/s, on NGO/PANI-GCE. Inset: Plot of Ipa, Ipc versus √ν……………………………………………………………………………..52 Fig 4.5 Cyclic Voltammograms for NGO/PANI-GCE in (i) pH 3, (ii) pH 4, (iii) pH 5, (iv) pH 6, (v) pH 7 phosphate buffer solution containing 1 mM Hydroquinone Inset: plot of Ipa vs pH. Scan rate = 100 mV/s………………………………………………………………………………….53 Fig 4.6: Cyclic Voltammograms for i) bare GCE ii) NGO-GCE iii) PANI-GCE and vi) NGO/PANI/-GCE, in phosphate buffer pH 4. Scan rate = 100 mV/s…………………………...54 Fig 4.7: Voltamograms of NGO/PANI-GCE in phosphate buffer ph 4 with increasing scan rate at (a) 50 mV/s, (b) 100 mV/s, (c) 150 mV/ s, (d) 200mV/s, (e) 250 mV/s, (f) 300 mV/s (g) 350 mV/s……………………………………………………………………………………………...55 Fig 4.8: Voltammograms of (a) Bare GCE b) NGO-GCE c) PANI-GCE d) NGO/PANI-GCE in 1mM Hydroquinone pH 4 phosphate buffers……………………………………………………56 Fig 4.9 Nyquist plots obtained for (i) Bare GCE, (ii) NGO-GCE, (iii) PANI- GCE, and (iv) NGO/PANI-GCE in 1 mM Hydroquinone in pH 4 phosphate buffer…………………………58 Figure 4.10 : Bode (phase angle versus log f) plots obtained for (i) bare GCE, (ii) NGO-GCE, (iii) PANI-GCE and (iv) NGO / PANI-GCE in 1mM Hydroquinone (pH4)……………………59 15 Fig 4.11: Effect of scan rate on peak potentials and currents a) 50 mV/s, b) 100 mV/s, c) 150 mV/s, d) 200 mV/s, e) 250 mV/s, f) 300 mV/s, g) 350 mV/s NGO/PANI-GCE for Hydroquinone oxidation. [Hydroquinone] = 1mM. Inset: plot of Ipa vs √v……………………………………..61 Fig 4.1.2 : Plot of potential versus log scan rate in 1mM Hydroquinon………………………..62 Fig 4.13: Plot of peak potential against pH for the detection of 1mM of Hydroquinone on NGO/PANI-GCE………………………………………………………………………………...63 Fig 4.14 Linear sweep voltammograms (a) 10 μM, (b) 20 μM, (c) 30 μM (d) 40 μM (e) 50 μM and 60 μM of phosphate concentrations in pH 4 PBS. Inset plot of Ipa vs. [Hydroquinone]. ………………………………………………………………………………...64 Fig 4.15 Langmuir adsorption isotherm plot for NGO/PANI-GCE in a) 10 µM, (b) 20 µM, (c) 30 µM (d) 40 µM (e) 50 µM and 60 µM of Hydroquinone concentrations in pH 4 PBS. Oxidation currents employed.……………………………………………………………………65 Fig 4.16 Chronoamperograms for different Hydroquinone concentrations. In PBS pH 4, a) 20 μM, b) c) 40 μM ,d) 60 μM , e) 80 μM and f) 100 μM Inset Ipa vs [Hydroquinone]………….67 Fig 4.17 : Plots of 𝐼𝑐𝑎𝑡 𝐼𝑏𝑢𝑓 vs. time (s) Fig 4.19 Plot of slopes2 vs. [Hydroquinone]…………………. Figure 4.17 : Plot of slopes2 vs. [Hydroquinone]………………………………………………69 Figure 4.21 ; DPV for NGO/PANI -GCE in: a) 0.2 μM, b) 0.4 μM, c) 0.6 μM, d) 0.8 μM, e) 1 μM, f) 1.2 μM, g) 1.4 μM, h) 1.6 µM. Inset: Plot of Ipa vs [Hydroquinone ]. …………………………………………………………………………………………70 16 Figure 4.22 continuous cyclic voltammetric evolutions for 1 mM Hydroquinone generated on GCE modified with NGO/PANI. Scan rate = 100 mV/s. pH 4 PBS……………………………………………............................................................................71 Fig 4.23: Differential pulse voltammograms for three repetitions in 1mM Hydroquinone in pH 4 PBS solution at NGO-PANI/GCE. Scan rate = 100 mV/s at potential 0.4 to 1.0 V……………..72 Fig 4.24 for (a) Hydrogen peroxide , (b) Mixed analytes, (c) hydroquinone (d) phenol…….73 17 Chapter 1 1.0 Introduction This chapter serves to highlight the background of the research and other techniques that were used in the determination of hydroquinone. The aims, objectives, problem statement and justification are of the study are also discussed. 1.1 Background Hydroquinone is an active ingredient in personal care products, food antioxidants, anthraquinone dyes, black white film developers and polymerization inhibitors [1]. It is also used in cosmetics and medical preparations. Dermal exposure is a result of the use of cosmetic and medical products containing hydroquinone, such as skin lighteners. Absorption via the skin is slower but may be more rapid with carriers such as alcohols. Hydroquinone , benzene 1.4 diol, Fig 1.1 is metabolized to p-benzoquinone and other oxidized products, and is detoxified by conjugation to monoglucuronide, monosulfate and mercapturic derivatives [2]. The excretion of hydroquinone and its metabolites is rapid and occurs primarily via the urine. Due to its physicochemical properties, hydroquinone will be distributed mainly to the water compartment when released into the environment. FIGURE 1: CHEMICAL STRUCTURE OF HYDROQUINONE 1 Different approaches such as spectrophotometry, high performance liquid chromatography, capillary electrochromatography, gas chromatography, fluorescence quenching and electro chemiluminescence, have been used to determine the concentration of hydroquinone [3]. It should be however be noted that the practical application of these methods is restricted by many disadvantages which include, formidable instrumentation, lengthy analysis time and tedious process [4]. As a conventional method, electrochemical analysis has played an important role in analytical chemistry due to the fast response, low instrument cost and feasibility for on-site measurement [4]. Much effort has been paid to develop the versatile electrodes to determine hydroquinone [4]. Typical examples are the modified electrodes, and the materials to decorate the surface adopt electrospun carbon nano fibers , L-cysteine oxide/gold , poly (thionine) [5], carbon nanotube-ionic liquid composite [5], Pt-MnO2 composite particle, graphitic mesoporous carbon , 1-butyl-3-methylimidazolium hexafluorophosphate (BMIMPF6) , copper hexacyanoferrate and platinum film [5]. Gold nanoparticles (AuNPs), due to its large surface area, high conductivity and electro catalytic capability, have been employed to increase the detection limit in electrochemical analysis [5]. In this research, a nitrogen doped graphene oxide decorated with polyaniline modified glassy carbon electrode (NGO / PANI -GCE) was fabricated and employed as the working electrode for hydroquinone determination. The combination of nitrogen doped graphene oxide nanoparticles (NGO NP) and polyaniline nanoparticles (PANI NP) firmly increased the electron transfer rate and the active area of the electrode. The experimental results indicated that the as-modified electrode exhibited excellent electrochemical catalytic activities towards the redox of hydroquinone. 2 1.2 Aims of the Research ⮚ Development of an electrochemical sensor for hydroquinone using glassy carbon electrode decorated with polyaniline and nitrogen doped graphene oxide. 1.3 Objectives ⮚ To synthesise nitrogen doped graphene oxide nanoparticles (NGO NPs) with polyaniline nanoparticles (PANI NPs). ⮚ To modify the glassy carbon electrode with nitrogen doped graphene oxide nanoparticles (NGO NPs), polyaniline nanoparticles (PANI NPs), and nitrogen doped graphene oxide nanoparticles decorated with polyaniline nanoparticles (NGO / PANI NPs). ⮚ To characterise the electrode modifiers, NGO Np, PANI Np and NGO/ PANI Np using FTIR, UV-Vis spectroscopy, Cyclic Voltammetry, and electrochemical impedance spectroscopy. ⮚ To determine the surface coverage of the modified electrode NGO / PANI - GCE by performing scan rate studies in 1mM Ferricyanide solution. ⮚ To carry out pH studies in phosphate buffer solution for the optimisation of pH for the analysis of hydroquinone using NGO / PANI – GCE electrode. ⮚ To carry out comparative studies on modified electrodes a) bare GCE, b) NGO-GCE, c) PANI - GCE, d) NGO / PANI-GCE in pH 4 phosphate buffer solution. ⮚ To evaluate the effect of pH, scan rate and concentration on peak currents and peak potentials. ⮚ To determine the electrode transfer kinetics, Tafel slopes, Langmuir adsorption isotherm, catalytic rate constants and relative catalytic effects of NGO / PANI - GCE. 3 ⮚ To determine the limit of detection of hydroquinone in pH 4 phosphate buffer solution by using differential pulse voltammetry and chronoamperometry. ⮚ To study the effect of interferences in the presence of hydroquinone on the NGO / PANI – GCE. ⮚ To carry out reproducibility and stability studies on the NGO /PANI - GCE towards the oxidation of hydroquinone in pH 4 phosphate buffer solution. 1.4 Problem Statement Hydroquinone is an organic pollutant which when absorbed through the skin and mucous membranes can cause damage to the lungs, liver, kidney and genitor urinary tract in the animals and human [5]. It is toxic to humans in concentrations that exceed 2 parts per million and it has relatively low difficult degradability, hence the industrial and clinical implications associated with it are a cause for concern [1]. This has sparked a growing need for safe detection procedures [1]. At present, the main determination methods are chromatography spectrophotometry and electrochemical methods [1]. Among all these techniques, spectrophotometry suffers from easy interference by related compounds and needs complicated pre-separation steps, which are unsuitable for multicomponent analysis [1]. Chromatography has potential for the detection of hydroquinone. It however also requires time-consuming sample pretreatment steps and expensive instruments [1]. Due to their merits of simple operation, prompt analysis and no need for complicated sample pretreatment, electrochemical methods have been developed as one of the most efficient alternatives in environmental analysis[1]. However, the direct determination of hydroquinone at conventional electrodes such as glassy carbon electrodes is difficult because the similar chemical structures lead to the overlap of their redox peaks [1]. In order to overcome this problem, many materials such as nano materials , transition metal compounds conducting 4 polymers , are widely applied to modify the electrodes. It is important to note that due to the exquisiteness and expensive nature of these instruments, they are not easily accessible. These expensive instruments are also associated with tedious complex time consuming and expensive sample pretreatment which requires qualified expert technicians to operate them. They have high detection limits and less sensitivity. Despite the effectiveness of conventional methods, they however have limitations; in that, they are very costly, time consuming, laboratory borne, they need a lot of skill in the operation and sometime suffer from low detection limit [6]. Furthermore, a large amount of sample volume and solvent are needed in separation and extraction procedures [6]. 1.5 Justification Formulations of personal care products that contain hydroquinone exposes a huge part of the populace to irritant defects caused by hydroquinone, hence it is important to come up with a user-friendly technique to detect it promptly on site [6]. The concern about the human health risks associated with the exposure to mutagenic, teratogenic and carcinogenic hydroquinone in the environment has brought about the interest in the development of a suitable method of analysis. The method should be cheaper and easier to use in identifying and quantifying [3]. Due to the problem of low detection limit of hydroquinone, an electro- chemical sensor, a super nanocomposite that is able to detect them at very minute concentration is made in this investigation. Presently, instrumental methods of analysis involving chromatographic (TLC, GC, HPLC), spectroscopic (UV-Vis, IR, MS) or coupled techniques (GC-MS), are heavily relied upon for environmental analysis. 5 Electrode modification improves the glassy carbon electrode s’ electro catalysis properties by lowering its potentials and increasing current and surface area towards determination of hydroquinone [7]. Polyaniline is an intrinsically conducting polymer that contains delocalised electrons and it confers its conducting properties on to the glassy carbon together with nitrogen to produce a synergistic super conducting electrode [7]. It has excellent environmental stability, ease of synthesis, low cost, high electrical properties (as a result of their delocalized π-π conjugated systems), Electroanalytical methods have low cost of instrumental requirements and better speeds of analysis. Electrode modification improves the glassy carbon electrode through lowering the potential and increasing the current and surface area hence the modifiers were combined together in order to reduce the over potential of the bare glassy carbon electrode and also to increase sensitivity towards the detection of hydroquinone [8]. 6 CHAPTER 2 LITERATURE REVIEW 2.0 Summary This chapter presents a literature review comprising of an outline on hydroquinone, nanocomposite based on polyaniline and nitrogen doped graphene oxide and their method of synthesis. Also, a background of the characterization techniques used are discussed as well as all of the theory of electrochemistry. 2.1 Hydroquinone Hydroquinone (1,4-benzenediol; C6H4(OH)2) is a white crystalline substance when pure, with a melting point of 173-174 °C [9]. The specific gravity is 1.332 at 15 °C, and the vapour pressure is 2.4 x 10-3 Pa (1.8 x 10-5 mmHg) at 25 °C [9]. It is highly soluble in water (70 g/litre at 25 °C) and the log n-octanol/water partition coefficient is 0.59 [3]. With respect to organic solvents, the solubility varies from 57% in ethanol to less than 0.1% in benzene [3]. Hydroquinone is combustible when preheated [4]. It is a reducing agent which is reversibly oxidized to its semiquinone and quinone. Hydroquinone (1,4-benzenediol; C6H4(OH)2) is a white crystalline substance when pure, with a melting point of 173-174 °C [4]. The specific gravity is 1.332 at 15 °C, and the vapour pressure is 2.4 x 10-3 Pa (1.8 x 10-5 mmHg) at 25 °C [4]. It is highly soluble in water (70 g/litre at 25 °C) and the log n-octanol/water respect to organic solvents, the partition coefficient is 0.59 [4]. With solubility varies from 57% in ethanol to less than 0.1% in benzene [4]. Hydroquinone is combustible when preheated. It is a reducing agent which is reversibly oxidized to its semiquinone and quinone [4]. 7 2.12 Reduction-oxidation equilibria Hydroquinone undergoes reversible redox changes which can involve a variety of pathways and redox couples. Each redox couple has an electrochemical potential dependent upon the degree of protonation and electron reduction [4]. quinone + 2 H+ + 2 e- Hydroquinone (2.1) Hydroquinone / Quinone redox couple implies the transfer of two electrons and two protons [3]. The rate of this process is determined by many factors among which electric conductivity of the polymer layer [3]. Graphene Oxide (GO) Carbon nanostructures have been widely been harnessed in numerous applications as a result of their excellent properties [10] . Carbon based nanomaterials such as carbon nanotube (CNT), fullerene and graphene have gained considerable interest due to their potential use as multifunctional materials and wide range of applications in different kind of devices [10]. Nano-science and nanotechnology primarily deal with the synthesis, characterization, exploration, and exploitation of nanomaterials. Graphene is the world’s thinnest, strongest, and stiffest material, as well as being an excellent conductor of heat and electricity. It is the basic building block of other important carbon allotropes [10]. Graphene is a single atomic layer of sp2 carbon atoms and as a single or one-atom-thick, two-dimensional crystal, graphene has been greatly considered as basic building block for all sp2 graphitic materials including fullerenes, carbon nanotubes, and graphite [10]. It can be wrapped 8 up into zero dimensional (0D) fullerenes, rolled into one dimensional (1D) nanotubes or stacked into three dimensional (3D) , Fig 2.1 [11]. The two-dimensional structure of graphene enables it to exhibit several unique properties which differ from other carbon nanomaterials. These include a high specific surface area of over 2,600m2/g [11], excellent electronic properties, current density, superior thermal conductivity , high mechanical and tensile strength [12], optical transmittance [13] and fascinating transport phenomena such as quantum Hall Effect [13]. The oxidation of graphene using strong oxidizing agents produces a hydrophilic graphene oxide material [14]. The aromatic lattice of graphene of graphene is disturbed by epoxides, alcohols, ketones and carboxylic groups [15]. In graphene oxide, the carbon layers in graphite are interspaced with oxygen molecules [13]. Lattice disruption is shown by the increase in interlayer spacing from 0.335 nm for graphite to more than 0.625 nm for graphene oxide Its structure has oxygen containing groups such as hydroxyl, carbonyl groups, carboxylic and epoxy group [16], Fig 2.1 9 FIGURE 2.1: FIGURE SCHEMATIC DIAGRAM OF STRUCTURE OF GRAPHENE OXIDE (GO) Graphene oxide gained more attention than graphene because it is easy to functionalize, easily labelled with fluorescent probe and is compatible with most biomolecules and can be encooperated into a conducting polymer matrix [16]. Graphene oxide has hydrophilic groups which expand the film property of modified electrodes [16]. Doping nitrogen on graphene oxide improves the process ability and sensing performances [17]. Graphene oxide can be dispersed in aqueous solutions [13]. 2.1.2 Graphene oxide preparation using modified Hummer’s method This method uses a combination of potassium permanganate and sulphuric acid Diamanganese heptoxide as the active specie. KMnO4 + 3H2S04 MnO3 + MnO-4 K+ MnO3 + H3O +3HSO-4 MNO7 (2.2) (2.3) The reaction of potassium permanganate with sulphuric acid produces a dark red oil. The bimetallic heptoxide is much more reactive than its monometallic tetra oxide counterpart, an is 10 known to detonate when heated to temperatures greater than 55 OC or when exposed to organic compounds [18], Fig 2.3 is a diagram of synthesis of GO from graphite flakes. FIG 2.3: GO SYNTHESIS 2.1.4 Properties of Graphene oxide Graphene oxide is a versatile compound that is able to be optimised and functionalised to suit different properties like hygroscopic, dispersibility and toxicity [10], the exact same sense why it is successfully doped with nitrogen. Excellent electrochemical performances are achieved as a result of electronic structure modification of graphene oxide, which promotes intrinsic electron transfer between the host substrate and electroactive materials. 2.1.5 Chemical reactivity of graphene oxide Graphene oxide is an insulator due to its disrupted sp2 bonding network, however its electrical conductivity can be conjured up by restoring the π – network. This is done through reduction especially on the epoxide group [20]. Doping nitrogen on graphene oxide is done through ring opening of the epoxy group under appropriate conditions. In covalent functionalization, substituted amines are introduced through this route [20]. Microscopic and very minute molecules can be grafted on the surface of graphene oxide via a grafting on to approach [23]. 11 Pre-formed poly vinyl alcohol, (PVA) is attached to carboxylic acid groups of graphene oxide platelets via ester linkages [20]. 2.1.6 Nitrogen doped Graphene oxide Nitrogen-doping increases the conductivity of graphene oxide by raising the Fermi level towards the conduction band compared with pristine graphene [8]. Nitrogen-doped graphene oxide nanocomposite (N-RGO) is prepared via a facile method, in which ethylene glycol and ammonia are used as the reducing agent and nitrogen precursor [8]. 2.2 Polyaniline Polyaniline is among the family of intrinsically conducting polymers (ICP), Fig 2.3 [2]. It has been extensively studied owing to the good environmental stability, ease of synthesis, low cost, high electrical conductivity, and mechanical flexibility exhibited by the polymer [25]. It has unique multiple oxidation states as well as acid /base doped/ de doping response which has made it an excellent for acid/base chemical vapor sensor [26]. All these properties have prompted its potential application in various devices such as super capacitors, sensor, electrochromic, actuators [2]. Other application includes its use for making electromagnetic shielding , antistatic coating and flexible electrodes [2] 12 Name of polymer Structure Conductivity Type of (S cm-1) doping Poly(acetylene) 200 -1000 n, p Polythiophene 10- 100 p 13 Polyaniline 5- 200 n, p FIGURE 2.3; INTRINSICALLY CONDUCTING POLYMERS 2.2.1 Structure and oxidation state of Polyaniline Emeraldine form of polyaniline is often referred to as base (EB), is neutral, if doped, ( the imine nitrogen has been protonated by an acid.) it is called emeraldine salt (ES), termed as protonation [25]. Emeraldine base is best considered as the most useful form of polyaniline , apart from been highly stable at room temperature, the doped form, which is emeraldine salt (ES),is highly electrically conducting [27]. The two other forms of polyaniline, leucomeraldine and pernigraniline are poor conductors, even in their doped state [28]. This transformation of polyaniline to different forms with different colours, apart from the oxidation state, showed part of the uniqueness in its properties compared to other polymers [2]. The emeraldine salt (green colour) obtained as the product from the polymerisation of aniline in acidic medium (electrolyte) [2]. Conductivity of polyaniline has provided its application in some devices such as supercapacitors electrochromic [29]. 2.2.2 Conductivity in polyaniline Conducting polymers (CPs) exhibit small perturbations at their surfaces and generate strong changes in their electroactivity which can be probed by amperometry or potentiometry [31]. Conducting polymers offer a modifying conducting surface that they is easy to functionalize with additional chemical functions [32]. The emeraldine form of polyaniline provides the opportunity to be protonated by doping to form a conducting form of emeraldine [2]. Reported 14 studies revealed that the degree of doping can actually determines the rate of conductivity, studies also reported that the highest conductivity of polyaniline can be attained at 50% degree of doping, which is associated with the emeraldine salt of polyaniline [33], and the conductivity level and variation in their order of magnitude to be 10-2 S cm-1 for undoped emeraldine and up to 103 S cm-1 for doped emeraldine [2]. 2.2.3 Synthesis of polyaniline The method of synthesis commonly adopted to prepare polyaniline is electrochemical and chemical oxidative polymerisation method. The chemical oxidative polymerisation method of synthesis, involving the presence of an oxidising agent in acidic medium [31]. 2.2.4 Doping in polyaniline The protonated emeraldine, produced during the oxidative polymerisation of aniline in aqueous acid, is electrically conducting due to the presence of the cation radical in its structure [11]. These positive charged units on the structure are then balanced by negative charged counterion (conjugated base) from any dopant such as chloride or sulphate ions which are usually inserted during electrochemical polymerisation and as well referred to as protonic acid doping [31]. However, the concentration of dopant from studies reported to have profound effect on the morphology, conductivity and electro-catalytic activity of polyaniline and the polarisation method [31]. 2.2.5 Polymer nanocomposites Polymer nano-composites (PNC) consist of a polymer or copolymer having nanoparticles or nano-fillers dispersed in the polymer matrix [11]. These may be of different shape platelets, fibres, spheroids), but one dimension must at least be in the range of 1–50 nm [34]. These 15 systems require orientation of the dispersed phase, controlled mixing/compounding, stabilization of the achieved dispersion, and the compounding strategies for all multi-phase systems, including PNC [35]. However, nanomaterial of conducting polymers is of special interest as their properties are considerably different from the properties of corresponding macroscopic materials [34]. Usually, a change in surface properties is observed when a conducting polymer is surrounded by a dopant, either nanomaterial or bulky substances such as nanotubes, nanoclusters, nanoparticle nano-cystals quantum dot, graphene oxide [36]. This however, forces the polymer backbones to interact with the molecules [32]. A nanocomposite with different morphology is formed and which is capable of solubilising the conducting polymer [11]. Nanomaterial of polyaniline can effectively provide a controlled electrochemical catalysis, orientation and solubilisation, as a result of the formation of micelles and obviously enhancing the quality of the polymer which has given them potential in application such as sensors [11]. Conducting polymer nanomaterial for a sensor construction has gained a lot of recognition owing to the large surface area dependent[31]. The yield strength and hardness of microstructure polycrystalline materials typically increases with decrease in size particles [30]. 2.2.6 Methods of preparation of polymer nanocomposite Methods used in the preparation of polymer nanocomposite include the sol−gel process [5] and monomer/polymer grafting to clay layers [11]. Others include melt method, solution mixing and in-situ intercalative polymerisation method [11]. 2.2.7 Amalgamation/ Solution Mixing of Nitrogen doped graphene oxide and Polyaniline Nitrogen doped graphene oxide and polyaniline are dispersed in DMF and vigorously shaked overnight until NGO sobubilises and fully dispersed into the polyaniline (PANI) matrix [11]. 16 2.3 Electrochemical Synergism The synergistic effect of a nitrogen-doped graphene oxide and the intrinsically conducting polymer polyaniline are explored and harnessed in a facile novel method that forms an exquisite nanocomposite electrochemical sensor [37]. Graphene oxide is doped using ethylene glycol as the reducing agent and ammonia water as nitrogen precursor [23]. The addition of nitrogen-doped graphene results in a high contact area between the electrolyte / electrode, which facilitates transportation of the electrolyte ion and electron into the inner region of the electrode [20]. Nitrogen-doping significantly improves the conductivity of graphene oxide, which is valuable in promoting electron transfer in electrochemical reactions [24]. Specifically, this in situ synthesis method assures the uniform distribution of polyaniline surfaces of NGO [38]. The NGO/PANI- nanocomposite exhibits not only high capacity, but also excellent rate capability [29]. 2.3.1 Electrode Modification Electrode Modification is whereby layers of electro active species are attached on to the electrode surface to enhance electron transfer reactions occurring on the surface [39]. The surface takes on the properties of the attached species [39]. Bare electrodes require large oxidation potential and so chemically modified electrodes (CMEs) reduce over potentials [40]. Glassy carbon electrodes, (GCE) is modified by intrinsically conducting polymer, (ICP) polyaniline and nitrogen doped graphene oxide, (NGO) in a novel facile method [41]. It results in improved electro-catalysis and freedom from the surface fouling effects. Alternatively, electrodes can be modified to prevent undesirable reactions from competing kinetically with the desired electrode process [39]. 17 Studies carried out in the past involving the use of carbon nanotubes for electrode modification unearthed striking electro catalytic properties [2]. Its integration on the electrode surface produced lower over potentials [42]. Polymer modified electrodes have the ability to catalyse electrode reactions and can significantly improve the electro-catalytic properties of the substrates, decrease the over potential, decrease the potential difference (ΔE), increase the reaction rate and improve the stability of the electrode response [5]. These electro-catalytic processes, proceeding at modified electrodes, present Carbon nanotubes are famed for their high sensitivity, a result of their unusual nanostructure, the reason why they are used for analyte detection [2]. The use of graphene oxide has attracted many researchers because of its sp3 hybridized material which exhibits a very larger surface area, many functional groups and it allows smooth electron mobility on its planar, making it an excellent modifier coupled with nitrogen-doping that also increases its conductivity by raising the Fermi level towards the conduction band compared with prisitin graphene [19]. 2.3.2 Characterisation of synthesized composite Infrared spectroscopy, IR Infrared spectroscopy is an important technique that provides easy way to identify the presence of certain functional groups in a molecule [43]. Also, the unique collection of absorption bands can be used to confirm the identity of a pure compound or to sense the presence of specific impurities [29]. In infrared spectroscopy, IR radiation is passed through a sample where some of the radiation is absorbed by the sample and some of it is passed through (transmittance) [11]. The resulting spectrum represents the molecular absorption and transmission, producing a molecular fingerprint of the sample [44]. Similar to a fingerprint, two unique molecular 18 structures cannot produce the same infrared spectrum. As a result, infrared spectroscopy can result in a positive identification (qualitative analysis) of every diverse kind of material [11]. Additionally, the size of the peaks in the spectrum is a direct indication of the amount of material present [37]. This makes infrared spectroscopy a useful technique for several types of analysis in terms of identifying an unknown material, determining the quality or consistency of a sample and the amount of component in a mixture [4]. A typical specta is illustrated in fig 2.4 below. FIGURE 2.4 TYPICAL FT-IR SPECTRA OF GRAPHENE OXIDE. Electrochemistry Electrochemistry is the study of production of electricity from energy released during spontaneous chemical reactions and the use of electrical energy to bring about non-spontaneous chemical transformations [45]. It involves the transfer of electrons between electrodes and 19 reactant molecules in a solution producing electric power [45]. The electrochemical techniques used involve a three-electrode system and the cell is monitored by a combination of a computer and a potentiostat / galvanostat [46]. A chemical reaction is brought about by application of excess voltage from an external power and the resultant current flow is measured to obtain the characteristic of the analyte under study [47]. 2.4 Voltammetry Voltammetry is a class of electrochemical method used in analytical chemistry and various industrial processes whereby, information about an analyte is obtained by measuring the current against the potential [6]. In a voltammetry technique, the common characteristic involves the application of a potential (E) to an electrode and the monitoring of the resulting current (I) flowing through the electrochemical cell [48]. The applied potential in many cases is varied or the current monitored over a period of time (T) [6]. Voltammetry techniques can be described as some function of E, I and T. Therefore, voltammetry can be generally defined as the investigation of three-dimensional space relating to potential (E), current (I) and time (T). At least two electrodes are required to conduct an experiment in voltammetry. The working electrode (WE), reference electrode (RE) and usually a counter electrode (CE) are the types of electrodes commonly used in voltammetry technique [49]. 2.4.1 Instrumentation The basic component of a modern electroanalytical technique for voltammetry comprises of the following; a potentiometer, a computer and the electrochemical cell. The types of the electrodes are, working, reference and counter electrodes [50]. 20 2.4.2 The potentiostat The working principle of a potentiostat actually depends on its connection to the electrochemical cell. It controls the potential of the counter electrode (CE) against the working electrode (WE) so that the potential difference between the reference electrodes (RE) is distinct, and agrees with the value specified by the user [51]. Therefore, in potentiostatic / galvanostatic mode, the current flow between the working electrode and the current is controlled [52]. The potential difference between the reference electrode and working, and the current flowing between the current and working electrode are constantly monitored [52]. 2.4.3 Electrodes Generally, an electrode provides the interface across which a charge can be transferred or where the effect of the charge can be felt like the working electrode (WE), which is where the action of interest takes place [52]. The electrode is an utmost important part of the system. The shape, size and style of modification on the surface, all depends on the application process [52]. 2.4.4 The reference electrode (RE) The reference electrode is an electrode with a steady and recognizable electrode potential [6]. It is used as point of reference to control and measure the potential of the other electrodes [53]. The saturated calomel electrodes (SCE), silver/silver chloride (Ag/AgCl) electrode are the most commonly used reference electrode for aqueous solutions [52]. 2.4.5 Counter electrode (CE) The counter electrode (also known as auxiliary electrode) is usually made of an inert material of platinum (Pt) or metallic foil, gold (Au), graphite or sometimes glassy carbon may be used [52]. Counter electrode does not usually take part in the electrochemical reaction, but the total surface 21 act as source of electron so that current can flow between the working electrode and counter electrode which make it not to be isolated from the reaction [52]. The surface area must however be higher than that of the working electrode so that it will not be a limiting factor in the kinetics of the process under investigation [11]. 2.4.6 Working electrode (WE) The working electrode is where the reaction or transfer of interest is taking place [48]. At an appropriate potential, oxidation or reduction of a substance on the surface of the working electrode will bring about a mass transport of a new material along with current been produced. The commonly used materials for working electrodes are glassy carbon (GC), platinum (Pt), gold (Au). Others include small mercury drop and film electrodes. The size and shape also varies and depends on application. The quality of an ideal working electrode includes a wide potential range, low resistance as well as a surface that is reproducible [11]. 2.4.7 Cyclic voltammetry The cyclic voltammetry is the most extensively used technique for acquiring qualitative information about electrochemical reactions [11]. It has the ability to rapidly provide considerable information on the thermodynamics of redox processes and the kinetics of heterogeneous electron-transfer reactions as well as the coupled chemical reactions or adsorption processes [6]. The current potential curve usually shows a peak at a potential where the oxidation or reduced reaction occurs whilst the height of the peak current could be used for the quantification of the concentration of the oxidation or reduction species [11] . 22 2.4.8 Illustration of a typical cyclic sweep voltammetry. In simple analysis, the surface is started at a particular voltage with respect to a reference half-cell such as calomel or Ag/AgCl, the electrode voltage then changes to a higher or lower voltage at a linear rate and finally changed back to the original value at the same linear rate [45]. When the surface becomes sufficiently negative or positive, a solution species might gain electrons from the surface or transfer electrons to the surface resulting in a measurable current in the electrode circuitry [45]. However, some important information can also be investigated from the parameters, this include whether the electrochemical process displayed by the sample is reversible, irreversible or quasi –reversible, and also give close information on how fast the electron process is, relative to other processes such as diffusion. For example, if the electron transfer is fast relative to the diffusion of electroactive species from the bulk solution at the surface of the electrode, the reaction is said to be electrochemically reversible, and the peak separation (ΔEp) is given by equation; ΔE = Epa- Epc = 2,303RT/nF (2.4) Where ΔEp is the peak separation (V), Ep,a is the anodic peak potential (V), Ep,c is the cathodic peak potential (V), n represent the number of electrons and F the Faraday constant (96 486 C mol-1), R is the gas constant (8.314 J mol-1 K-1) and T is the absolute temperature of the system (298 K) [11]. Therefore, number of electrons (n) involved in the electrochemical process can be estimated from the above equation [8]. Therefore, for a redox couple that is reversible, the cyclic voltammograms has been studied to have the following defined characteristics; The expression; ΔE = Epa -Epc = 59/n mV (2.5) Determines the voltage separation between the current peaks. 23 The ratio of the peak currents is always equal to one: Ipa/Ipc =1 (2.6) The formal potential Eo' for a reversible redox couple is easily determined as the average of the two peak potentials : Eo' = (Epa + Epc)/2 (2.7) The peak currents are usually proportional to the square root of the scan rate (Ip is proportional to ʋ½) Quantitative information regarding analyte concentration, that specifies the anodic peak current, (Ip,a) and cathodic peak current (Ip,c) in terms of analyte concentration, C [11]. The scan rate (mV s-1) of the process is varied, ( how rapidly the electroactive specie is diffusing through the solution to and from the surface of the working electrode), is obtained from the voltammograms using Randles- Sevcik equation [51], Ip = -0.4463nF [nF/ RT]1/2 T*D ½ vA (2.8) Where, n is number of electrons appearing in the half-reaction for the redox couple, ʋ is the rate at which potential is swept, F is the Faradays constant (96485 C mol-1), A, the electrode area (cm2), R represent the universal gas constant (8.314 J mol-1 K-1), T is the absolute temperature (K), D is the diffusion coefficient analyte (cm2 sec-1) and Γ⃰ represents the surface concentration of the adsorbed species on the modified electrode [54]. If temperature is assumed to be 25 0C (298.15 K), the equation can be written as [51], Ip =2.69 ×105 n 3/2 AD ½ CO 2.8.1 24 An illustration of a cyclic voltammetry (CV) for the reduction of 1 mM ferricyanide in 0.1 M KCl at glassy carbon electrode, scan rate; 100 mV s-1 is shown in in Fig 2.5 [11] . The peak shape of the oxidative and the reverse reductive current versus electrode potential is typical of an electrode reaction in which the rate is governed by diffusion of the electroactive species to a planar electrode surface. (Ip,a and Ip,c) are the anodic and cathodic peak respectively [51]. Typical cyclic voltammogram for a reversible reaction Plotting the peak current against the square root of the scan rate, the slope of the linear plot can be used to estimate the diffusion coefficient according to the Randles-Sevcik equation shown above [55]. At this instance, the log of peak current versus the log of scan rate gives a linear plot whose slope distinguishes between diffusion controlled peaks, adsorption peaks or even a mixture of the two [55]. For diffusion peak, a plot of the Log ip versus log ʋ is linear with a slope of 0.5 and a slope of 1 for an adsorption peak [11] . Intermediate values of the slope are 25 sometimes observed, and suggested to be a “mixed” diffusion-adsorption peak [11]. The surface concentration of the adsorbed material is estimated by the use of the Brown-Anson model equation; Ip = n 2 F 2T*Av / 4RT 2.8.2 Where Ip, n, F, A, R, v, T and Γ⃰ (the surface concentration of the adsorbed species of the electrode modifier) are all expressed in the equations above [11]. It is important to note that, in a sensor operation, some parameter such as potential scanning rate, operating temperature and diffusivity of the reactant are very necessary [56]. The peak current may be used to quantify the concentration of the reactant of interest provided, that the effect of concentration on the diffusivity is negligible [4]. Differential Pulse Voltammetry The sensitivity of cyclic voltammetry is considerably low hence the aim of pulsed voltammetric methods is to lower detection limits [57]. The relationship between current and concentration gives quantitative information about the system studied and this can be clearly seen if diffusion controls the current magnitude [11]. In differential pulse voltammetry (DPV) fixed voltage pulses are superimposed on a linear potential ramp and are applied to the working electrode at a period of selected time just before the potential pulse drops [57]. The current is measured twice which at a point just before the pulse is being imposed and then again just before the pulse begins to drop [57]. In DPV when a potential pulse is applied to an electrode the capacitive current flows proportionally to it but decays exponentially with time [57]. The magnitude of the faradaic current decreases as an exponential function versus (t)1/2 [58]. 26 Linear sweep voltammetry Linear sweep voltammetry is a voltammetric method where the current at a working electrode is measured while the potential between the working electrode and a reference electrode is swept linearly in time [59]. Oxidation or reduction of species is registered as a peak or trough in the current signal at the potential at which the species begins to be oxidized or reduced [57]. Linear sweep voltammetry can identify unknown species and determine the concentration of solutions [59]. E1/2 can be used to identify the unknown species while the height of the limiting current can determine the concentration. The sensitivity of current changes vs. voltage can be increased by increasing the scan rate [57]. Higher potentials per second result in more oxidation/reduction of a species at the surface of the working electrode [58]. Chronoamperometry Chronoamperometry is an electrochemical technique in which the potential of the working electrode is stepped and the resulting current from faradaic processes occurring at the electrode (caused by the potential step) is monitored as a function of time [57]. Limited information about the identity of the electrolyzed species can be obtained from the ratio of the peak oxidation current versus the peak reduction current [57]. However, as with all pulsed techniques, chronoamperometry generates high charging currents, which decay exponentially with time as any RC circuit [60]. Chronoamperometry is a very powerful method for the quantitative analysis of a nucleation process [60]. This useful technique leads to obtain the initial information about nucleation and growth mechanism in a studied system [5]. Additionally, the amount of charge for deposition (dissolution) can be determined [60]. Also, this method can be applied for the determination of a nucleation rate constant and an adsorption isotherm [4]. With the chronoamperometry, the 27 current is measured versus time as a response to a (sequence of) potential pulse [60]. The recorded current can be analyzed and its nature can be identified from the variations with time [60]. Electrochemical impedance spectroscopy EIS is a perturbative characterization of the dynamics of an electrochemical process [61]. Electrochemical impedance is the response of an electrochemical system (cell) to an applied potential [60]. The frequency dependence of this impedance can reveal underlying chemical processes [61]. It is regarded as a derivative of linear sweep voltammetry or staircase voltammetry, with a series of regular voltage pulses overlaid on the potential linear sweep or stair steps [61]. The current is measured instantaneously before each potential change, and the current difference is plotted as a function of potential [62]. The Nyquist plots obtained in electrochemical impedance spectroscopy comprise of a straight line and a semi-circle [63]. The diameter of the semicircle corresponds to the charge transfer resistance and diffusion controlled process respectively [61]. The straight line portion represents the Warburg impedance which takes into account the frequency dependence on diffusion transportation to the electrode surface [64]. Bode Plots The nature of the Bode plots confirms the structural differences between the bare electrode and modified electrodes [62]. Bode plots, shows a well- defined symmetrical peak for the bare electrode at particular angle and corresponding frequency representing the relaxation process at the electrode solution interface [65]. This relaxation process shifts to different phase angles and 28 frequencies on modification of the electrode [62]. Theseshifts indicate that the reactions are now occurring at a modified surface rather than the bare electrode [65]. 2.5 Electro-catalysis Electro-catalysis can be defined as a process whereby, an electro-catalyst participate as a catalyst in electrochemical reaction [56]. The electro-catalyst can be a specific form of catalyst that function at the surface of the electrode or may be the surface of the electrode itself [42]. The catalyst materials modify and increase the rate of chemical reaction without being consumed in the process. The process can be heterogeneous, which involve chemical reaction occurring at the surface of the electrode and electron transfer usually takes place at the interface, leading to a new product formation (in catalytic electro-synthesis), or homogeneous reaction which is a sequence of reactions that involve a catalyst in the same phase as the reactants [23]. However, a homogeneous catalyst is most commonly co-dissolved in a solvent with the reactants (coordinating complex or enzymes) [66]. The ability to catalyse some reaction is one of the most outstanding properties of conducting polymers [42]. The kinetics of electrode processes of some solution specie is able to be improved by a thin layer of a conducting polymer, deposited onto the surface of a substrate electrode [45]. These electro-catalytic processes, proceeding at a conducting polymer electrode is presently yielding application in various fields of electrochemistry [54]. Three processes are considered to be happening during the electro-catalytic conversion of solution species at conducting polymer modified electrode [55]. Firstly, heterogeneous electrons transfer between the electrode and a conducting polymer layer, and electron transfer within the polymer film [48]. This process is normally accompanied by the movement of charge compensating anions and solvent molecules within the conducting polymer film [48]. Many factors determine the rate of 29 this process and which include, electric conductivity of polymer layer, electron self-exchange rate between the chains/or clusters of polymer, and anion movement within polymer films also seems to be greatly significant [48]. Secondly, the diffusion of solution species to the reaction zone, where the electro-catalytic conversion occurs [48]. Unlike simple electrode reaction, this process can be more complicated in cases where the electro-calytic conversion occurs within the polymer film [48]. In that case, the diffusion of species within the film, in addition to the possible electrostatic interaction of this specie with the polymer film should be taken into account [67]. In the third process, a chemical (heterogeneous) reaction takes place between solution species and conducting polymer [67]. Electro-catalysis takes place when the transfer of electrons between the hydroquinone and NGO / PANI- GCE surface. In this regard, the catalyst on the modified electrode becomes oxidised in the electrolyte and then interacts with the analyte which are mostly in their reduced state. There is electron process taking place which leads to the oxidation of the analyte and simultaneous reduction of the catalyst [69]. 2.5.1 Chemically modified electrode Chemically modified electrode (CMEs) involves an approach to electrode system design that finds application in electrochemical investigation [69]. It includes the relationship of heterogeneous electron transfer and chemical reactivity of electrode surface chemistry, electron and electrostatic phenomena at electrode surface, as well as ionic transport phenomena in polymers [70]. A chemically modified electrode allows a thin film of selected conducting material to be bounded on its surface for the purpose of improving the chemical, electrochemical, optical, 30 electrical, transfer of electron and other desirable properties of the film in a rational chemically designed manner [64]. Therefore, the significant drive for modifying electrode surface is electro-catalysis of the electrode reaction of an analytical desired substrate. It is often observed that redox reaction of an analyte on a naked electrode surface using voltammetry techniques such as cyclic voltammetry or square wave voltammetry are slow, so that oxidation or reduction occurs at a potential that is greatly higher than positive or negative, respectively, than the expected thermodynamic potential [18]. Such situation can be sorted by accelerating the desired reaction with an immobilized mediator catalyst [64]. The mediator is attached on the surface of the electrode to function as facilitator for the charge transfer between the analyte and electrode [64]. The oxidised form of the mediator catalyst is rapidly reduced, and then, its reduced form reacts with the analyte specie in solution [64]. It can then be indicated that the electron transfer occurred between the mediator and the electrode and not between electrode and the analyte, directly. From the illustrated equation below, a mediator can be represented by M and the analyte, A, Mox + ne Mred + A ox Mred 2.8.3 Mox + A red 2.84 31 CHAPTER 3 EXPERIMENTAL 3.0 Introduction The chapter gives information on materials and different experimental procedures employed for the preparation of an electrochemical sensor based on nitrogen doped graphene oxide modified with polyaniline. Electrochemical characterization of hydroquinone was evaluated using cyclic voltammetry, impedance spectroscopy, bode plots, linear sweep, differential pulse voltammetry and chronoamperometry. Parameters like pH and scan rate were investigated to evaluate the applicability of the NGO / PANI – GCE in the electro catalysis of hydroquinone. 3.1 Equipment F.T.I.R. Spectra were obtained using Thermo scientific Model equipped Model with OMNIC software. UV – Vis spectroscopy was used for characterization. Sonicator model KQ- 20B was used for agitation of samples. All electrochemical experiments were performed using Auto lab potentiostat PG STAT302N equipped with NOVA version 1.10 software and encompassed with a three electrochemical cell made up of glassy carbon electrode, platinum wire counter and a Ag|AgCl reference electrode. Samples were dried in tan oven drier. Weighing of samples was done using OHAUSE analytical balance. pH measurement was done using the pH meter, PHS -3C model. 32 3.2 Chemicals and reagents Chemicals used in this study were of analytical grade and were used without further purification. Potassium ferrocyanide and potassium Ferricyanide, aniline (C6H5NH2), ammonium persulphate, ammonium chloride (NH4Cl), sodium hydroxide(NaOH), dimethyformamide (DMF), potassium bromide (KBr), hydrochloric acid (HCl, 37%), hydrogen peroxide (H2O2, 35 wt% water solution), sulphuric acid (H2SO4), sodium nitrite (NaNO2), potassium permanganate (KMnO4), hydroquinone, di- potassium orthophosphate (KH2PO4), orthophosphate, (K2HPO4) and potassium di-hydrogen Polishing pads and alumina micro powder (1.0, 0.3 and 0.05 μm alumina slurries) were used for polishing the glassy carbon electrode (GCE). 3.2.1 Synthesis procedures Synthesis of Polyaniline Aniline was first distilled to remove impurities. The aniline (0.2 M) was dissolved in 10 mL of 1 M HCl aqueous solution. While maintaining vigorous stirring at room temperature ammonium peroxydisulfate (APS 0.05 M) was dissolved in 10 mL of 1 M HCl to form an oxidant solution [25]. The oxidant solution was then quickly poured into the aniline solution at room temperature followed by immediately magnetic stirring for 2hours. Polymerization can be observed when green color of PANI emeraldine salt became visible. The stirring was stopped after 2hours and left undisturbed to react for 24hours. After which the precipitated polymer was collected by filtration and repetitively washed with water ethanol and hexane until the filtrate became colorless. Polyaniline sample was collected having been dried at 60○C, Fig 3.1 [25]. Oxidation of aniline hydrochloride with ammonium persulfate to yield polyaniline (emeraldine) hydrochloride salt [27]. 33 Synthesis of Polyaniline nanoparticles Fig 3.1 Assumed possible mechanism of polymerization of aniline monomer to polyaniline 3.2.2 Graphene oxide Graphene oxide nanoparticles were synthesized using the improved modified Hummers’ method, a slightly modified method of the original hammers’ method in Fig 3.2 34 Fig 3.1: Synthesis of graphene oxide nanoparticles Graphite flakes (2 g) and NaNO3 (2 g) were mixed in 90 mL of H2SO4 (98%) in a 1000 ml volumetric flask kept under at ice bath (0-5.C) with continuous stirring. 2. The mixture was stirred for 4 hours at this temperature and potassium permanganate (12 g) was added to the suspension very slowly. The rate of addition was carefully controlled to keep the reaction temperature lower than 15 oC. The mixture is diluted with very slow addition of 184 ml water and kept under stirring for 2 hours [20]. The ice bath was then removed, and the mixture was stirred at 35°C for 2 hrs. The above mixture is kept in a reflux system at 98°C for 10-15 minutes. After 10 minutes, the temperature was changed to 30°C which gave a brown colored solution. Again after 10 min, it was changed to 25°C, and maintained the temperature for 2 hrs. The solution was finally treated with 40 ml H2O2 by which color changed to bright yellow. An aliquot of 200 ml of water is taken in two 35 separate beakers and equal amount of solution prepared is added and stirred for 1 hr. It was kept without stirring for 4 hours, where the particles settled at the bottom and remaining water is poured to filter. The resulting mixture was washed repeatedly by centrifugation with 10% HCl and then with deionized (DI) water several times until it formed a gel like substance (pHneutral). After centrifugation the gel like substance is vacuum dried at 60°C for more than 6 hrs to GO powder [71]. 3.2.3 Doping Nitrogen on Graphene oxide and modification with polyaniline A mass of fifty milligrams of GO NPs was added to 60 mL of ethylene glycol under sonication for 4 hours to obtain a well-dispersed GO NPs suspension [72]. An aliquot 10 mL of ammonia solution was added and vigorously stirred for 10 minutes, polyaniline in DMF solution (0.75 mL) was also added under vigorous stirring for 2 hours at the room temperature, and then heated at 95◦C for 7 h. The precipitate was isolated by filtration then washed with ethanol and deionized water. It was then dried at 80◦C overnight. Highly crystalline N-GO / PANI NPs composite was obtained [71]. 3.3 Characterization of the chemical modifiers and the composite 3.3.1 Fourier Transfer Infrared Spectroscopy (FTIR) All the synthesized compounds GO NPs, PANI NPs and NGO/PANI NPs were characterized by FTIR. A mass of 0.0100 g of the respective samples were mixed in a mortar and pestle and combined with 1g KBr to form a pellet and this was characterized within the range 400 - 4000 cm-1. 36 3.3.2 UV -Vis Spectroscopy The synthesized nanoparticles, (GO NPs), and (PANI NPs), (0.005g) were dissolved in 10 mL dimethyformamide (DMF) and experimental wavelength were scanned between 200 to 700 nm [11]. 3.3.3 Electrode modification The BCGE was polished with alumina paste on Buehler Felt pads and ultrasonically cleaned in ethanol for about 5 min. The electrode was further cleaned in water for about 5 min then finally rinsed with distilled water to ensure there are no impurities or interferences, and then dried in the sun. A mass of 0.1 g of the prepared conjugates was dissolved in a volume of 5 mL of DMSO and these solutions were sonicated for 30 min. The cleaned BCGE was modified using the drop and dry method using NGO, PANI and NGO / PANI in 1ml DMF. The electrode was dipped in solution of the modifiers in DMSO [73]. 3.3. 0 Buffer solution prepaparation 18.000 g/mol dipotassium hydrogen phosphate and 14.000 g/mol potassium hihydrogen phosphate was taken and made up to 200 ml using distilled water to make the buffer. The designated pH was reacted by adjusting the pH using sodium hydroxide ( 0.1 M) and hydrochloric acid (0.1 M) [74]. 3.4 Hydroquinone analysis A volume of 1mM of Hydroquinone solution was prepared by 0.150 g diluted to 1000ml with phosphate buffers in the pH range between 3 to 8. 37 3.5 Electrochemical characterization 3.5.1 Electrochemical behavior of modifiers in 1 mM [Fe (CN)36]3-/4 solution Cyclic voltammetry was used for the investigation of electron transfer kinetics for the bare GCE, NGO-GCE, PANI-GCE and NGO/PANI-GCE. The study was carried out in 1 Mm [Fe (CN)6] 3-/4 solution at a scan rate of 100 mV/s from -0.4 to 0.6 V. 3.5.2 Electrochemical impedance spectroscopy and bode plots Electrochemical impedance spectroscopy and bode plots were carried out in 1 mM [Fe (CN)6]3-/4 solution for bare GCE, NGO-GCE, PANI-GCE and NGO/PANI-GCE in order to confirm the electron transfer resistance of the electrodes in correspondence to results obtained in cyclic voltammetry. Bode plots and electrochemical impedance spectroscopy occurs at the same time during analysis but in separate windows. 3.5.3 Scan rate studies in in 1mM [Fe (CN)6]3-/4 solution Scan rate studies were performed in 1 mM [Fe (CN)6]3-/4 solution by using NGO/PANI-GCE electrode in order to determine the surface coverage of the modified electrode. Scan rate range was from the range of 100 to 350 mV/s from -0.4 to 0.6V. 3.6 Optimisation of parameters 3.6.1 Effect of pH The effect of pH was studied in the range from pH 3 to 8. Adjusting of the buffer solution was carried out with dilute concentration of 0.1 M NaOH and 0.1 M HCl. The studies were carried out by preparing 5 volumetric flasks (100ml each) with different pH phosphate buffer solution containing 1 mM of hydroquinone. The studies were carried out in cyclic voltammetry by using NGO/PANI-GCE electrode. The studies were performed by scanning the electrode from 0.0 to 0.9V at a fixed scan rate of 100 mV/s. 38 3.6.2 Comparative studies in pH 4 phosphate buffer solution Comparative studies were performed in pH 4 phosphate buffer solution containing 1mM hydroquinone. The studies were carried out by using modified electrodes a) Bare GCE, NGO-GCE, PANI-GCE and NGO/PANI-GCE in order to confirm the reduction in potentials and increase in anodic peak currents on the oxidation of hydroquinone. Cyclic voltammetry was used for this study. The studies were performed by scanning each electrode from 0.0 to 0.9V at a fixed scan rate of 100 mV/s. 3.6.3 Scan rate studies in pH 4 phosphate buffer solution Scan rate studies were carried out in-order to determine the effective surface coverage of the modified electrode NGO/PANI-GCE. There studies were done in pH 4 phosphate buffer solution by using NGO/PANI-GCE modified electrode. Cyclic voltammetry was used for this study. The studies were performed by scanning NGO/PANI-GCE electrode from 0.0 to 0.9V at a fixed scan rate ranging from 100 to 350 mV/s. 3.7 Kinetic studies Kinetic studies were carried out in 1mM hydroquinone solution in pH 4 phosphate buffer. The studies were performed in cyclic voltammetry by using NGO/PANI- GCE modified electrode. The studies were performed by scanning NGO/PANI-GCE electrode from 0.0 to 0.9V at a fixed scan rate ranging from 100 to 350 mV/s. 3.8 Langmuir adsorption isotherm studies Linear sweep studies were carried out in order to determine the Langmuir adsorption isotherm of hydroquinone on the surface of NGO/PANI-GCE. The study was performed by using working standard solutions of hydroquinone 10 µM, 20 µM, 30 µM, 40 µM, 50 µM and 60 µM prepared 39 from serial dilution of 1mM hydroquinone in phosphate buffer solution pH 4. The working standard solution were prepared in 100ml volumetric flask and diluted to the mark with pH 4 phosphate buffer solution. The response behavior was observed on NGO/PANI-GCE. The studies were performed by stirring the electrode for 10 minutes and scanning the electrode from 0.0 to 0.9V at a fixed scan rate of 100mmV/s . 3.9 Catalytic rate constant Chronoamperometric studies were performed in order to determine catalytic rate constant was of hydroquinone on the surface of NGO/PANI-GCE. The studies were performed by preparing working standard solutions of 20 µM, 40 µM, 60 µM, 80 µM and 100 µM form 1mM stock solution of hydroquinone in pH 4 phosphate buffer solutions. The working standard solution were prepared in 50ml volumetric flask and diluted to the mark with pH 4 phosphate buffer solution. The prepared working standard solutions were filled in the electrochemical cell respectively and the behavior was observed on NGO-PANI/GCE. The studies were performed by scanning the electrode at different potentials 0.00V, 0.8 and 0.8. The electrode was scanned for 25 seconds at fixed scan rate of 100mV/s. 3.10 Differential pulse voltammetry Differential pulse voltammetry is a sensitive technique that was used to determine the limit of detection and limit of quantification. The study was carried out by preparing working standard solution of 0.2µM, 0.4µM, 0.6µM, 0.8µM, 1.0µM, 1.2µM, 1.4µM and 1.6µM from 1mM stock solution of hydroquinone in pH 4 phosphate buffer. The working standards were prepared in 100ml volumetric from flask and diluted to mark with pH 4 phosphate buffer solutions. The prepared 100ml solution of working standards was placed in the electrochemical cell respectively. Before analysis each solution was purged with nitrogen for 10minutes prior to 40 analysis and then the behavior was observed on NGO/PANI-GCE electrode. Parameters: initial potential 0.00V, final potential 0.90V, step potential 0.00500V, modulation amplitude 0.0500V, initial time 0.5s and scan rate 0.100 V/s. 3.11 Stability studies Stability studies was performed on NGO/PANI-GCE in 1mM hydroquinone solution phosphate buffer pH 4 by performing 20 continuous in cycles by using cyclic voltammetry technique at 0.1V/s scan rate at 0.2 to 1.0V. 3.12 Reproducibility studies NGO / PANI - GCE was analyzed in a solution containing 1mM of Hydroquinone solution by employing the DPV technique. Before and after each analysis the electrode was washed using distilled water in order to remove adhered particles at a scan rate of 0.01 V/s. potential of 0.2 to 1.2 V and amplitude of 0.05 V for a period of about 3 times. Effect of interference Interference studies were investigated using DPV technique. 1 mM of hydroquinone was detected in the presence of hydrogen peroxide and phenol which are assumed to interfere with detection of hydroquinone. Equimolar solutions of interfering analytes were prepared in the same matrix with hydroquinone in phosphate buffer solution pH 4. The mixture was analyzed from 0 to 1.2 V potential and amplitude of 0.05 V. 41 CHAPTER 4 RESULTS AND DISCUSSION Introduction The chapter highlights all the results and findings obtained from the research. The obtained results are discussed in detail and compared to work published by other researchers. 4.1 F.T.I.R characterisation 42 Fig 4.1 FT-IR Spectrum of (a) GO , (b) , PANI , (c) NGO- PANI Nps The FTIR spectrum shows the stacked spectra of graphene oxide, polyaniline and nitrogen doped graphene oxide decorated with polyaniline (NGO/PANI NPs) 4.1 NGO / PANI Np FTIR NGO / PANI Np spectra at (a) shows the presence of the quinoid ring and the benzoid ring shifts to 1599.29 cm-1 and 1492 cm-1, respectively. These could be attributed to the inco-operation of the polyaniline matrix into the graphene oxide lattice. Further the C-N stretching vibrations which appeared at 1143.61 cm-1 in PANI where shifted to 1599.29 cm-1 in NGO/PANI. The C-H stretching in polyaniline shifted from 755.70. to 617.37 cm-1. Shift of bands were a result of formation of the Graphene oxide-nitrogen complex. Figure 4.1.2 Graphene oxide FTIR Graphene oxide was characterized by FT-IR. Spectra were obtained from 4000-400 cm-1 region [9]. According to the literature of Graphite, no distinct peaks are detected in graphite however 43 graphene oxide (GO) showed collections of peaks corresponding to the following functional groups: C=O (cm-1), aromatic C=O (1646 cm-1), carboxyl C-O (1406 cm-1), epoxy, alkoxy C-O (1000 cm-1), hydroxyl O-H (3500 cm-1). The appearance of the collection of the functional peaks gave an indication that the original extended conjugated orbital system of the graphite powder was destroyed during the oxidation process and oxygen containing functional groups has been inserted into the carbon skeleton according to literature. Figure 4.1.3 Polyaniline FTIR The FTIR spectrum of PANI, shows the characteristic at 1658 .79. and 1464.61 cm-1 are assigned to the C=C stretching of quinoid ring and benzenoid rings respectively. The characteristics peaks at 1202.60 and 1143.61 cm-1 are attributed to the C-N stretching vibration of the secondary aromatic amine group and aromatic C-H in plane bending vibration respectively [47]. The peak at 765.70 cm-1 represent C-H the small peak at 606.26 cm-1 represented para-distributed aromatic rings indicating polymer formation. 44 Fig 4.1.3 UV- visible spectra of graphene oxide A maximum absorption peak at around 245 nm is observed for GO in the UV visible spectra, which corresponds to the π-π⃰ transition of aromatic C-C bonds. Literature highlights that the absorption peak is well around 230 nm hence the obtained absorption peak is well in range. Figure 4.1.4 Pani UV-Vis 45 Literature highlights the presence of two bands at 590–690 (π*←n transitions –quinone-imine groups- exciton transition of the quinoid rings), and 290–390nm (π*← π transitions) , to π-π* transition of the benzenoid rings and the other due to charge transfer excitations of the quinoid structure which are characteristic of emeraldine base [27] . 4.2 Electrochemical characterisations Voltammetric studies in 1.0 mM [Fe (CN)6]3-/4- in 1M KCl Figure 4.2: Cyclic voltammograms for: a) bare GCE b) NGO- GCE c) PANIi-GCE d) NGO/PANI- GCE in 1 mM [Fe (CN)6]3-/4- solution. Scan rate = 100 mV/s Cyclic voltammetry was used for the investigation of electron transfer kinetics for the bare GCE, NGO-GCE, PANI-GCE and NGO-PANI-GCE. The study was carried out in 1 mM [Fe (CN)6] solution at a scan rate of 100 mV/s from -0.6 to 0.8 V. 46 ΔEp values of working electrodes Electrode ΔEp values / V BGCE 0.40 NGO-GCE 0.19 PANI-GCE 0.18 NGO- PANI -GCE 0.16 Electrodes gave peak potential differences with the following trend; NGO/PANI-GCE < PANI-GCE< NGO-GCE< BGCE. The NGO/PANI-GCE exhibited the best electron transfer kinetics as compared, better than the other electrodes. The lower Ep for NGO/PANI-GCE compared to the rest of the modifiers electrode is possibly due to the linkages between the NGO and PANI as well as their good alignment on the electrode surface which makes, electron exchange between the redox probe and electrode modifier much faster confirming its improved electron transfer compared with the rest of the modified electrodes. The electron transfer kinetics of the modifiers on the surface of glass carbon were also confirmed by the increase in anodic peak current the order of electron transfer is therefore Bare -GCE (𝐼𝑃𝑎: 88 ×10-5 A) > NGO-GCE (𝐼𝑃𝑎: 126 ×10-5 A)> PANI-GCE (𝐼𝑃𝑎: 170 ×10-5 A) > NGO-PANI-GCE (𝐼𝑃𝑎: 332 ×10-5 A). The increase in peak current for NGO/PANI-GCE as compared to other electrodes is due to improved flow of pie electrons on the surface of nitrogen doped graphene oxide. A high surface area as well as good conductivity possessed by NGO/PANI-GCE can also 47 be attributed to the catalytic properties of nitrogen doped graphene as a result of its higher surface-to-volume ratio which allows accessibility surface to polymer matrix [24], hence a more enhancement compared to PANI –GCE. The large Ep for NGO-GCE implies that on its own, it has poor electron transfer properties, however when coupled with polyaniline, its catalytic properties are activated as evidenced by the pronounced decrease in Ep separation. This is explained in terms of the electron donating nature of PANI which reduce the redox potentials. It should also be equally noted that NGO has better electron kinetics than BGCE, a property attributed to the nitrogen for pumping electrons in the GO lattice. The amide linkage formed between NGO and PANI facilitates the easy flow of electrons to and from the linked NGO molecule. Improved electron transfer kinetics is also a result of the nanostructured sizes of the conjugates which enables them to provide a large surface area for the transfer of electrons. NGO/PANI-GCE showed better electron transfer properties. 4.3 Electrochemical impedance spectroscopy Electrochemical impedances spectroscopy (EIS) measurements in [Fe(CN)6]3-/4 solution using 0.1 M KCl as the supporting electrolyte were investigated to assess the electron transfer properties of the modified glassy carbon electrode. 48 Fig 4.3 Nyquist plots obtained for a) bare GCE b) NGO-GCE c) PANI -GCE d) and e) NGO/PANI -GCE in 1mM [Fe(CN)6] solution in 1M of KCl. Inset is the Randles circuit model used in fitting data. Fig 4.3 shows a Nyquist plots for bare-GCE, NGO-GCE, PANI-GCE and NGO/PANI -GCE. The Nyquist plot data was fitted using Randles equivalent region (electron-transfer properties) and low frequency region (electrolyte diffusion controlled properties). The region of interest to this work is the high frequency region which is the kinetically controlled region and will give us the kinetics of the modified bare glassy carbon electrode. Kinetically controlled region in the Nyquist plot is of high importance since it shows the semi-circle which is related to the charge –transfer resistance (RCT). The smaller the RCT, the more conducting the electrode or the materials used to modify the electrode [75]. The RCT value for a bare electrode surface was 113.9 kΩ cm-2 and this value was 86.5 kΩcm-2 on NGO-GCE, 65.4 kΩcm-2 PANI-GCE and 58.2 kΩcm-2 on NGO-PANI-GCE. The Rct value was the smallest at NGO-PANI-GCE compared to 49 all other electrodes. The decrease in Rct values at NGO-PANI-GCE is attributed to (i) PANI and NGO being a good conductor of electrons. Table 4.2 Charge transfer resistance values of modified electrodes R c t ( kΩ cm-2) Electrode BARE GCE 113.9 NGO-GCE 86.5 PANI-GCE 65.4 NGO/PANI-GCE 58.2 50 Bode plots in 1.0 mM Fe(CN)6 3–/4– aqueous solution using 0.1 M KCl as the supporting electrolyte. Figure 4.4 Bode (phase angle versus log f) plots obtained for i) bare GCE ii) NGO-GCE iii) PANI -GCE iv) and v) NGO/PANI -GCE in 1mM [Fe(CN)6] solution in 1M of KCl Bode plots were used to obtain frequency related information, which cannot be obtained from their Nyquist plots. The nature of the Bode plots confirmed the structural differences of the GCE modified electrodes and the bare GCE [40]. The bare GCE showed unsymmetrical peak with a maximum phase angle value of 53o corresponding to the relaxation process of the GCE / hydroquinone interface. After modification of GC electrode with NGO, PANI, and NGO/PANI, all the peaks shifted towards lower frequencies for the relaxation processes of the modifier –GCE / hydroquinone interfaces, with the PANI spectrum showing a broad band which stretches from lower frequencies to higher frequencies. The relaxation process of the NGO/PANI-GCE / Hydroquinone was at a phase angle of 67O. Changes in phase angle and frequencies confirmed 51 that the oxidation of hydroquinone was taking place at modified platform rather than on the bare GCE surface. Both the Nyquist and the Bode plots confirmed the poor electron transfer kinetics for the NGO-GCE for hydroquinone. Such a trend was also observed from the cyclic voltammetry of hydroquinone on different electrode where NGO/PANI-GCEs showed reduced potentials and improved currents. At the frequency region of the impedance under study the charge transfer Rct, decreased for the electrode modifiers due to facilitation of the electron transfer which is an indication that films form high electron conduction pathways between the electrode and electrolyte / analyte [76]. The phase angles values for all electrode surfaces studied in this work are less than the ideal 90○ for a true capacitor. The bare GCE had a phase angle at 53○ corresponding to the GCE/ hydroquinone interface. 4.4 Surface area determination The surface area of NGO/PANI-NPs GCE was determined in 1 mM K3[Fe(CN)6]3-/4 by applying the Randles –Sevcik Equation [77]. Ip= (2.69 × 105) n3/2D1/2CAeffv1/2 (4.0) where ip the peak current, n is equal to the number of electrons transferred at the surface of the electrode Fe(CN)63- + e- Fe(CN)64- (4.1) As a result , n is equal to 1, D is the diffusion coefficient of the analyte in solution 7.6 × 10-6 cm2/s-1 and C is the solution concentration in (mol/cm-3),Aeff is the effective surface area and v is the scan rate (V/s-1). Based on this, ip is proportional to v1/2 and produces a linear plot with slope m given by the equation 52 m = (2.69 × 105)n3/2 Aeff D1/2C (4.2) Figure 4.3 shows the obtained voltammograms at different scan rates from (a) 50 mV/s, (b) 100 mV/s, (c) 150 mV/s, (d) 200 mV/s, (e) 250 mV/s, (f) 300 mV/s and (g) 350 mV/s. The plots of peak current, 𝐼𝑃 for both anodic and versus square root of scan rate (𝑣 1/2 ) (Figure 4.2 insert) 2 were linear (𝑅 = 0. 9984 and 0.9902) , signifying a diffusion –controlled redox process [78]. Fig 4.3 Effect of scan rate on peak potentials and currents (a) 50 mV/s, (b) 100 mV/s, (c) 150 mV/s, (d) 200 mV/s, (e) 250 mV/s, (f) 300 mV/s, (g) 350 mV/s, on NGO/PANI-GCE. Inset: Plot of Ipa, Ipc versus √ν. The NGO/PANI-GCE had an effective surface are of 0.13 cm2 comparing with known surface area of bare electrode of 0.0712 cm2 [8]. This indicates that the modified electrode displayed a large surface area for electro catalysis. 53 4.5 Optimization of parameters 4.5.1 Effect of pH pH is one of the factors affecting oxidation of hydroquinone. Fig 4.5 Cyclic Voltammograms for NGO/PANI-GCE in (i) pH 3, (ii) pH 4, (iii) pH 5, (iv) pH 6, (v) pH 7 phosphate buffer solution containing 1 mM Hydroquinone Inset: plot of Ipa vs pH. Scan rate = 100 mV/s. pH studies where carried out to probe the best pH for oxidation of hydroquinone in the range between pH three up to eight. The best peak current maximum response was obtained at pH four. The plot of pH against current showed that as the pH changed from pH 4 to lower acidic values, 54 the peak current would decrease. Under basic pH, the peak current was very low and almost insignificant [6]. 4.6 Comparative study in pH 4 buffer Voltammograms of the bare and modified electrodes i) bare GCE) NGO-GCE ii) PANI-GCE iii) NGO/PANI-GCE vi were obtained by scanning the electrodes in pH 4 phosphate buffer solution at a scan rate 100 mV/s. Fig 4.6: Cyclic Voltammograms for i) bare GCE ii) NGO-GCE iii) PANI-GCE and vi) NGO/PANI/-GCE, in phosphate buffer pH 4. Scan rate = 100 mV/s. The performance of the electrodes was evaluated in pH buffer four without an analyte and as expected there were no peaks but however, NGO/PANI-GCE rather showed excellent catalysis with lower initial oxidation potential better than the other electrodes as shown by the graph. 55 4.7 Scan rate studies in pH 4 phosphate buffer solution without an analyte Fig 4.7: Voltamograms of NGO/PANI-GCE in phosphate buffer ph 4 with increasing scan rate at (a) 50 mV/s, (b) 100 mV/s, (c) 150 mV/ s, (d) 200mV/s, (e) 250 mV/s, (f) 300 mV/s (g) 350 mV/s 4.8 Comparative study in 1 mM hydroquinone in pH 4 PBS 4 Comparative studies in 1mM hydroquinone was carried out for all electrodes Bare-GCE, NGO-GCE, PANI-GCE and NGO/PANI - GCE in order to observe the reduction in potential and increase in anodic peak current on the electro catalysis of hydroquinone. 56 Fig 4.8: Voltammograms of (a) Bare GCE b) NGO-GCE c) PANI-GCE d) NGO/PANI-GCE in 1mM Hydroquinone pH 4 phosphate buffers. The voltammograms indicate that current is increasing in the order, BGCE< NGO-GCE< PANI-GCE< NGO/PANI-GCE. The oxidation of hydroquinone initially occurs at a lower potential on the NGO/PANI-GCE electrode. NGO/PANI-GCE also shows a gradual definite peak rise unlike the other electrodes showing peaks which are less pronounced and defined. The pronounced peak rise in NGO/PANI-GCE is attributed to the synergistic effect of nitrogen doped graphene oxide with intrinsically conducting polymer Polyaniline. Peak currents, Initial Oxidation potential and peak oxidation potential for all probes, in 1mM hydroquinone. 57 Table 4.3 Electrode Initial Oxidation Peak Oxidation Current Potential Potential, E/V (A) BCGE 0.790 0.81 5 × 10-4 NGO-GCE 0.734 0.54 2.94 × 10-4 PANI-GCE 0.695 0.81 8.23× 10-4 NGO/PANI-GCE 0.625 0.82 1× 10-3 The values in the table above show that there is an increase in the peak current from BGCE to NGO/PANI-GCE. The distinctive peak current can be attributed to the spectacular synergistic conductivity between NGO and PANI. Graphene oxide of NGO provided a large surface area for electro catalysis together with the projection of different functional groups that project in the composite [15]. The peak and initial oxidation potential of NGO/PANI-GCE for the oxidation of hydroquinone showed that it is the best electrode as compared to other electrodes used in the past researches. Previous researches for the electrochemical determination of hydroquinone were done using hydroxyapatite modified glassy carbon electrode and the oxidation potential was 0.92 V 58 Comparing with previous studies, NGO/PANI-GCE is the best electrode for the determination of hydroquinone. 4.9 Electrochemical impedance Spectroscopy in 1 mM Hydroquinone in pH 4 PBS A three-electrode electrochemical impendence spectroscopy (EIS) was used to probe the redox and structural features of the different working electrodes (WE). Fig 4.9 shows the Nyquist plots obtained in 1 mM hydroquinone. The bare GCE, NGO–GCE, PANI-GCE and NGO/PANI-GCE displayed identical semi-circular Nyquist plots with straight line portion at lower frequencies. Fig 4.9 Nyquist plots obtained for (i) Bare GCE, (ii) NGO-GCE, (iii) PANI- GCE, and (iv) NGO/PANI-GCE in 1 mM Hydroquinone in pH 4 phosphate buffer. The electrochemical behavior of the four electrodes was further investigated using the electrochemical impedance spectroscopy (EIS) in 1.0 mM hydroquinone. The Nyquist plot in the 59 Figure above of the four electrodes comprised of semicircles and straight-line portions. The diameter of the semicircle corresponds to the charge transfer resistance and diffusion controlled process respectively [6]. The straight-line portion represents the Warburg impedance which takes into account the frequency dependence on diffusion transportation to the electrode surface [6]. The representative circuit for the Nyquist plots shown by insert, where Rs, CPE, Rct and W represents the solution resistance, a phase element, the charge transfer resistance and the Warburg impedance respectively. The order of decrease of electron transfer efficiencies is BCGE<NGO-GCE<PANI-GCE< NGO/PANI-GCE. This trend correlates with the one in cyclic voltammetry study where NGO/PANI-GCE showed the best reduced potentials and the best improved currents. 4.10 Bode Plots in 1mM hydroquinone Figure 4.10 Bode (phase angle versus log f) plots obtained for (i) bare GCE, (ii) NGO-GCE, (iii) PANI-GCE and (iv) NGO / PANI-GCE in 1mM Hydroquinone (pH4). 60 A plot above shows frequency which cannot be obtained from the nyquist plot. Surfaces with the phase angle shifted towards lower frequencies in the bode plot further confirms better catalytic activity of efficiency; hence the Bode plot further confirms better catalytic activity of the modified surface towards the oxidation of Hydroquinone. Electrode Phase angle Log Frequency BCGE 66.9 3.4 NGO-GCE 65.9 2.1 PANI-GCE 52.6 2.0 NGO/PANI-GCE 51 1.9 4.11 Kinetic studies of hydroquinone The effect of varying scan rate of 1 mM hydroquinone at NGO/PANI-GCE was studied and increase in peak current and shifts in peak potentials towards more positive values were observed for the conjugate as the scan rate increases from 100 to 350 mV/s. This is an indication of irreversibility of the redox reaction. The plot of current against square root of scan rate showed a linear relationship, with a correlation value of 0.995 showing that the electro-catalytic oxidation of hydroquinone is diffusion controlled Fig 4.11 61 Fig 4.11: Effect of scan rate on peak potentials and currents a) 50 mV/s, b) 100 mV/s, c) 150 mV/s, d) 200 mV/s, e) 250 mV/s, f) 300 mV/s, g) 350 mV/s NGO/PANI-GCE for Hydroquinone oxidation. [Hydroquinone] = 1mM. Inset: plot of Ipa vs √v. Tafel slopes Fig 4.1.2 shows a linear plot of peak potential, Ep versus log v. An increase in scan rate from 100 to 450 mV/s resulted in the hydroquinone oxidation peak shifting towards positive potentials, indicating the chemical irreversibility of the electro-catalytic oxidation process. The relationship between peak potential and scan rate for an irreversible diffusion process is graphically shown below. 62 Fig 4.1.2 : Plot of potential versus log scan rate in 1mM Hydroquinone Plots of Ep versus log v gave a linear relationship as represented by the Eq. Tafel slope of 326 mV decade -1 (2 × slope of plot was obtained for hydroquinone. Tafel slopes of this magnitude have no kinetic meaning but could indicate a passivated phenomenon occurring on the electrode surface. Tafel slopes much greater than the normal 30-120 mV decade-1 for a one electron rate determining step have been observed and have been either to chemical reaction coupled to electrochemical steps or to substrate catalyst interactions in a reaction intermediate. Mechanism of hydroquinone oxidation with NGO / PANI-GCE The number of electrons involved in hydroquinone oxidation at the NGO/PANI -GCE surface was obtained from a plot of oxidation against pH of hydroquinone solution 63 Fig 4.13: Plot of peak potential against pH for the detection of 1mM of Hydroquinone on NGO/PANI-GCE. From the plot above, it was observed that the peak potential decreased gradually with increasing pH values, with a slope of 58 m V/pH. The slope is indicating that the process is a two-electron transfer process. 64 Linear Sweep Studies Linear sweep voltammetry (LSV) was done to show adsorption behaviour of NGO/PANI-GCE Fig 4.14 Linear sweep voltammograms (a) 10 μM, (b) 20 μM, (c) 30 μM (d) 40 μM (e) 50 μM and 60 μM of phosphate concentrations in pH 4 PBS. Inset plot of Ipa vs. [Hydroquinone]. 65 Langmuir adsorption isotherm plot for NGO/PANI-GCE Langmuir adsorption isotherm plot for NGO/PANI-GCE in a) 10 µM, (b) 20 µM, (c) 30 µM (d) 40 µM (e) 50 µM and 60 µM of Hydroquinone concentrations in pH 4 PBS. Oxidation currents employed. Fig 4.15 Langmuir adsorption isotherm plot for NGO/PANI-GCE in a) 10 µM, (b) 20 µM, (c) 30 µM (d) 40 µM (e) 50 µM and 60 µM of Hydroquinone concentrations in pH 4 PBS. Oxidation currents employed. Fig 4.15 shows LSV plots obtained after keeping the electrode in a stirred solution for 10 minutes to allow for adsorption. Applying the Langmuir adsorption theory (Eq 4.8) a plot of the ratio of hydroquinone concentration to catalytic current against concentration of hydroquinone 66 gave a linear plot which is which can be interpreted as an adsorption controlled electrochemical process. [𝐻𝑦𝑑𝑟𝑜𝑞𝑢𝑖𝑛𝑜𝑛𝑒] 𝐼𝑐𝑎𝑡 = 1 ß𝐼𝑚𝑎𝑥 + [𝐻𝑦𝑑𝑟𝑜𝑞𝑢𝑖𝑛𝑜𝑛𝑒] 𝐼𝑐𝑎𝑡 (4.8) where ß is the adsorption equilibrium constant, 𝐼𝑚𝑎𝑥 is the maximum current and 𝐼𝑐𝑎𝑡 is the catalytic current. From the slope and the intercept of Fig 4.16 the adsorption equilibrium constant 3 ß was established to be 1. 4 ×10 𝑀 −1 . Using equation 4.9 which relates Gibbs free energy ○ ○ change due to adsorption (Δ𝐺 ) to the adsorption equilibrium constant ß, (Δ𝐺 ) was found to be -10.42kJ. This value is in comparable to those reported elsewhere for high Tafel slopes [79]. ○ (4.9) Δ𝐺 =− 𝑅𝑇 𝑙𝑛 ß Where R is the molar gas constant and T is room temperature 4.16 Chronoamperometric Studies Catalytic rate constants are measures of how fast redox processes proceed at the electrode / analyte interface. The rate of oxidation of hydroquinone was evaluated on NGO/PANI-GCE through Chronoamperometric studies. 67 Chronoamperograms for different Hydroquinone concentrations Fig 4.16 Chronoamperograms for different Hydroquinone concentrations. In PBS pH 4, a) 20 μM, b) c) 40 μM ,d) 60 μM , e) 80 μM and f) 100 μM Inset Ipa vs [Hydroquinone] 68 Plots of 𝐼𝑐𝑎𝑡 𝐼𝑏𝑢𝑓 vs. time Fig 4.17 Plots of 𝐼𝑐𝑎𝑡 𝐼𝑏𝑢𝑓 vs. time (s) Fig 4.19 Plot of slopes2 vs. [Hydroquinone]The rate constant for the detection of hydroquinone was calculated using the equation (kCO t) ½π Plot of slopes2 vs. [Hydroquinone] 69 𝐼𝑐𝑎𝑡 𝐼𝑏𝑢𝑓 = π1/2 Figure 4.17 Plot of slopes2 vs. [Hydroquinone] The rate constant for the detection of hydroquinone was calculated using the equation: 𝐼𝑐𝑎𝑡 𝐼𝑏𝑢𝑓 1 = π 2 (𝑘𝐶𝑂𝑡) 1/2 (4.10) Where Icat and Ibuf are currents in the presence and in the absence of Hydroquinone, k is the catalytic constant (M-1s-1) for the hydroquinone oxidation and t is the time in seconds’. Fig 4.19. Shows the linear relationship for the Icat and Ibuf vs t1/2 plots for different hydroquinone concentrations obtained from the Chronoamperograms. Fig 4.20 showed the linear relationship for the slope2 vs. [Hydroquinone]. The slope of Figure 4.20 is equal to πk and this gives a k value of 3.9 ×10 -7M-1s-1. The value of k obtained is large. The larger the k value, the faster the rate of oxidation at the modified electrode. This showed that NGO/PANI-GCE was the best electrode for fast detection of hydroquinone. Figure 4.18 insert shows the plot of peak current against concentration. A linear relationship was observed from the plot. 70 Differential Pulse Voltammetry is a very sensitive technique that was used to determine limit of detection using NGO-PANI-GCE in different concentrations of hydroquinone. DPV for NGO/PANI -GCE Figure 4.21 DPV for NGO/PANI -GCE in: a) 0.2 μM, b) 0.4 μM, c) 0.6 μM, d) 0.8 μM, e) 1 μM, f) 1.2 μM, g) 1.4 μM, h) 1.6 µM. Inset: Plot of Ipa vs [Hydroquinone ]. Figure 4.21 inset shows the plot of peak current against concentration. A linear relationship was −5 observed from the plot. A linear regression equation was obtained as 𝑖𝑝 = 88. 6𝑥 + 1 ×10 and R2 = 0.9926 where 𝑥 is the concentration of the analyte. The limit of detection is equivalent to 3σ/𝑠 where σis the standard deviation of the intercept and s is the slope of the calibration curve. LOD was found to be 1.03569 × 10-7. The LOQ (10σ/𝑠)was found to be 3.4531 × 10 -7 M. In a previous study on the voltammetric determination of hydroquinone in cosmetics the LOD 71 was found to be 2.3× 10-5 µM, comparing with our obtained results, the NGO/PANI-CE is a better electrode in the detection of hydroquinone. Stability Figure 4.22 continuous cyclic voltammetric evolutions for 1 mM Hydroquinone generated on GCE modified with NGO/PANI. Scan rate = 100 mV/s. pH 4 PBS The peak current is initially high and it gradually decreases as the number of cycles continues with the highest decrease between the first and the second scan and the drop in current eventually becomes very small showing the passivation of the electrode. The rate at which current drops is a measure of resistance to passivation of the electrode towards the analyte [5]. There is highest increase in the oxidation potential of the first and second scan. The sharp increases eventually become small. The oxidation potential of the first scan is lower than the second scan but it as the cycle continues it becomes uniform, and constant showing passivation of the electrode. This electrode fouling could be attributed to the polymeric film that is formed by Hydroquinone radicals on the electrode surface [6]. 72 Reproducibility The modified surface area provided better reproducibility as indicated by the slight decrease in the peak current after washing the electrode two different times with ethanol with relative standard deviation of 2.58 % and 4.22 %, which is below 5 % and this indicated good repeatability of the modified electrode [75]. Fig 4.23: Differential pulse voltammograms for three repetitions in 1mM Hydroquinone in pH 4 PBS solution at NGO-PANI/GCE. Scan rate = 100 mV/s at potential 0.4 to 1.0 V Interference Studies The interference study was done using DPV on NGO / PANI - GCE and the concentration of the interfering compounds was carried in a 1:1:1 ratio of hydroquinone: hydrogen peroxide : phenol Peaks were recorded for the hydroquinone alone, hydrogen and phenol alone then finally the three analytes were mixed in a 1:1:1 ratio and DPV voltammograms were recorded, Figure 4.24. 73 Fig 4.24 for (a) Hydrogen peroxide , (b) Mixed analytes, (c) hydroquinone (d) phenol The effect of the interfering analytes was determined using DPV and it was observed that there is relevantly no significant change in the peak currents and peak potentials of the hydroquinone. The relative percentage response of the sensor calculated using the formulae: 𝑅 % = [ 1 − (𝐼 𝑎𝑛𝑎𝑙𝑦𝑡𝑒 + 𝐼𝑖𝑛𝑡𝑒𝑟÷𝑖𝑛𝑡𝑒𝑟) ] × 100 Where I analyte and I interferents are the peak currents hydroquinone and for the interfering analytes respectively. The RSD % above 10 % shows that the compound interferes with the analyte [8]. All the interferences showed to have no effect as they had interference effect of less than 10 %, demonstrating an excellent tolerance to interference of the modified electrodes. 74 CHAPTER 5 5.0 Introduction The chapter concludes the work done in the research and suggests recommendations with reference to future study. 5.1 Conclusion A new electrochemical sensor based on GCE modified with NGO/PANI composite was successfully prepared, characterized and utilized for electrochemical determination of hydroquinone. The PANI nanoparticles showed enhancement on the sensitivity of the modified electrode considerably by increasing the conductivity and effective electroactive surface area of the electrode. The electrochemical conductivity and adsorption ability of the added layer was used as a sensing platform for hydroquinone. The NGO/PANI-GCE showed a wider linear range and a lower detection limit. NGO/PANI – GCE can be used to lower glassy carbon electrode over potentials in the determination of hydroquinone. The electrode surface area after modification is 0.13 cm 2.The rate constant, k is 3.9 × 10 -7 showing fast and excellent electron transfer during oxidation. LOD determined is 1.03569 × 10 -7 M and LOQ determined is 3.45 × 10 -7 M. 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Electrochim Acta 2016. doi:10.1016/j.electacta.2016.02.166. 85 86 APPENDICES APPENDIX A: MATERIALS List A: Apparatus used in synthesis and characterisation Erlenmeyer flask, Buchner funnel, distillation flask, measuring cylinders(25ml,50ml,100ml) ,volumetric flasks(50ml,100ml,250ml,500ml, 1000ml), micropipette, beakers, spatula, pestle ,mortar, wash bottles, conical flasks, petri dishes, burettes, filter papers, vials Table A1; Reagents and chemicals Name Chemical formulae Manufacturer Concentratio n Distilled water H2O MSU Lab Hydrochloric acid HCL Sigma aldrich 32 % Potassium K3[ Fe (CN)] 6 ACE 10M Sodium hydroxide NaOH Skylabs 0.1M Sulphuric acid H2SO4 ACE 0.1M Aniline C6H5NH2 Unichem 0.2 M Hydrogen peroxide H2O2 ACE 0.1 M Sodium nitrite Na3 NO ferricyanide 87 Ammonium NH4S2O3 Skylabs 0.05 persulphate Table A2 : Instrumentation Name Model Manufacturer Use in lab Analytical balance JJ224BC G&G Weighing pH meter Az -8601 Thermoscientif pH measurement Sonicator KQ -250B China Corp Agitation Potentiost PG stat 302N Autolab Electroanalysis FTIR Nicolet 6700 Thermoscientic Characterisatio n UV -vis UV 1700 Shimadzu Absorbance measurement Treatment of Glassware Laboratory detergents were used to wash glassware after which they were rinsed with distilled water to remove contaminants and impurities. This minimizes interferences that during electro analyses. 88 APPENDIX B: Working electrodes B1: Working electrodes used in this study Electrode modifier Method of modification Bare Glassy Carbon Electrode Electrode designation BCGE Nitrogen doped graphene oxide Drop and dry NGO-GCE polyaniline Drop and dry PANI -GCE Nitrogen doped graphene oxide Drop and dry NGO/PANI-GCE decorated with polyaniline 89 APPENDIX C: Calculation C1: Effective Surface area Constant R = 8.314 Jmol-1, T = 273 K 5 Randle-sevick equation 5 3 1 𝑚 = (2. 69 ×10) 𝑛 2 𝐴𝑒𝑓𝑓 𝐷2 𝐶2 Ip = (2.69 x 105) n3/2AD1/2V1/2C −6 D= 7.6 × 10-6cm2/s, C= 1×10 −5 cm2, m=1×10 2 and Aeff = 0. 13 𝑐𝑚 Limit of Detection and Limit of Quantification Excel Linest function Slope Intercept Standard error of the slope Standard error of the intercept R2 Standard error in y LOD = 1.035569 × 10-7 M LOQ = 3.4531 × 10 -7 M 90