Construction of functional and robust cobalt phthalocyanines modified electrodes for the electrocatalytic detection of metal-based and pharmaceutically derived pollutants.

Abstract

Water pollution has become a detrimental global concern in a world that continues to grow through industrialisation, population, and demand in sales from agricultural and pharmaceutical industries. It is therefore imperative for innovative methods of continuous water monitoring to be implemented to avoid the harsh effects that pollution poses to human, animal and environmental preservation. Advances from traditional analytical methods have been made to combat associated drawbacks such as tedious sample preparation, high maintenance costs, and lack of mobility. Electrochemical sensors can be used for the analysis of a vast range of water pollutants while offering on-site, simple analysis and inexpensive fabrication. Metallophthalocyanines have been utilised extensively as electrode modifiers due to their excellent redox properties and stability which can be fine-tuned by alteration of the metal centre and substituents. In addition, thes3e alterations improve selectivity, solubility and immobilisation onto electrode substrates. This research is aimed at the application of gold electrodes modified with CoPc-cou nanoconjugates and CoPc-cou electrospun nanofibers (ENFs) for the electrocatalytic detection of pollutants, paraquat and mercury, in real water samples. Experimental chapter one explores the optimization and application of a gold-modified electrode, CoPc-cou-f-MWCNTs/3-HT|Au, for the electrocatalytic detection of a water pollutant, paraquat (PQ). It was fabricated via a sequential modification procedure entailing the formation of self-assembled monolayers (SAMs) of a nanocomposite comprising of a coumarin tetra-substituted cobalt phthalocyanine (CoPc-cou) and carboxylic acid functionalized multiwalled carbon nanotubes (f-MWCNTs). This was followed by the in-situ immobilization of poly(3-hexylthiophene) ([3-HT]n) through electropolymerisation to render the chemically modified electrode (CME). Subsequently, the CME illustrated enhanced sensitivity towards PQ compared to the bare or CoPc-cou-f-MWCNTs modified electrodes. The CoPc-cou-f-MWCNTs/3-HT|Au electrode displayed a linear PQ detection range of 0.193 – 1000 μM with a limit of detection (LOD) and limit of quantification (LOQ) of 0.193 μM and 0.584 μM, respectively. Comparison between calibration curves for the modified electrode and HPLC-MS illustrates that the former method has a lower but comparable calibration sensitivity for PQ. In addition, this CME could electrocatalytically distinguish PQ within a real water sample collected from the Durban lagoon. Furthermore, the direct recovery of PQ in the lagoon water by the modified Au electrode was found to be 86%, which is lower than the calculated value of 97% obtained by HPLC-MS after rigorous solid-phase microextraction of the analyte. However, the lower percentage recovery could be rationalized by the interference studies. In experimental chapter two fabricated electrospun nanofibers containing CoPc-cou, polyaniline (PANI) and poly-vinyl alcohol (PVA) were used to modify a gold substrate which was subsequently immobilised using a 5% Nafion solution affording the CoPc-cou-ENFs-Nf|Au modified electrode. Comparison of the chemically modified electrode with the bare and other modified electrodes under optimised conditions displayed superior detection of mercury (Hg(II)) attaining a linear range of 10 – 3000 μM and an LOD and LOQ of 0.14 μM and 0.46 μM, respectively. This can be attributed to the affinity between Hg(II) and the mercaptocoumarin substituent (Hg-S) as well as the higher surface area occupied by the ENFs resulting in an increased number of active sites. Furthermore, the chemically modified electrode exhibit selectivity and sensitivity in an interference sample containing multiple heavy metals (Pb2+, Cd2+ and Hg2+). A good percentage recovery of 96% was attained when the CoPc-cou-ENFs-Nf|Au electrode was applied to a real water sample which was comparable to a percentage recovery of 98% which was attained using the ICP-OES to analyse the same water samples.