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Development of a passive, in situ, integrative sampler for monitoring biotoxins in aquatic ... PDF

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COPYRIGHT AND CITATION CONSIDERATIONS FOR THIS THESIS/ DISSERTATION Attribution — You must give appropriate credit, provide a link to the license, and indicate if o changes were made. You may do so in any reasonable manner, but not in any way that suggests the licensor endorses you or your use. NonCommercial — You may not use the material for commercial purposes. o ShareAlike — If you remix, transform, or build upon the material, you must distribute your o contributions under the same license as the original. How to cite this thesis Surname, Initial(s). (2012) Title of the thesis or dissertation. PhD. (Chemistry)/ M.Sc. (Physics)/ M.A. (Philosophy)/M.Com. (Finance) etc. [Unpublished]: University of Johannesburg. Retrieved from: https://ujdigispace.uj.ac.za (Accessed: Date). Development of a Passive, in situ, Integrative Sampler for Monitoring Biotoxins in Aquatic Environments Hlengilizwe Nyoni A thesis submitted to the Faculty of Science, University of Johannesburg, in fulfilment of the requirements for the Doctoral degree in Science (Chemistry) Supervisor: Prof Titus A.M. Msagati Co-supervisor: Prof Bhekie B. Mamba University of Johannesburg, September 2015 ABSTRACT This thesis focuses on functionalising the silicone membrane by filling it with synthesised γ-Fe O nanoparticles for the purpose of using it as a passive sampling 2 3 device for monitoring microcystins and cylindrospermopsin in aquatic environments. The identity and purity of the synthesised nanoparticles was verified by X-ray diffraction (XRD), transmission electron microscopy (TEM), scanning electron microscope (SEM), surface zeta potential analyser and Brunauer-Emmet-Teller (BET). There was no chemical uptake of microcystin compounds into the silicone membrane without a suspension of maghemite nanoparticles. But, a linear uptake of microcystin compounds was observed into the functionalised silicone membrane passive sampler throughout the exposure period. These findings suggest that the silicone membrane filled with a suspension of synthesised γ-Fe O nanoparticles can be an efficient, green 2 3 and less costly instrument useful in estimating biotoxin concentrations in South African waters and the world at large. This novel device was calibrated for the measurement of microcystin and cylindrospermopsin concentrations in water. The effect of temperature and hydrodynamics on the sampler performance was studied in a flow-through system ii ABSTRACT under controlled conditions. The chemical uptake of microcystins (MCs) and cylindrospermopsin (CYN) into the passive sampler remained linear and integrative ii ABSTRACT throughout the 28 days exposure. The rate of accumulation of most of the MC compounds tested was dependent on temperature and flow velocity. The use of performance reference compounds (PAHs and 13C labelled polychlorinated biphenyls) spiked into the newly developed silicone membrane / γ-Fe O nanoparticle passive 2 3 sampler, Chemcatcher and POCIS improved the semi quantitative nature of water concentration estimates in natural water. The corrected sampling rate values of model biotoxin compounds were used for calculations of time-weighted average concentrations in natural water. Further, a field study to test the newly developed sampler’s performance alongside commercially available Chemcatcher (polar version), Polar organic chemical integrative sampler (pharmaceutical configuration) and solid phase extraction technique (grab sampling) was conducted. The developed novel sampling device was employed for the measurement of time-weighted average concentrations of cylindrospermopsin (CYN) and microcystins (MCs) in natural cyanobacterial water blooms of the Hartbeespoort dam. Data obtained by the three passive sampling devises provided a more relevant picture of the situation and enabled better assessment of potential risks. The results suggested that the three sampling devices are suitable for use in monitoring microcystin and cylindrospermopsin concentrations in aquatic environments. iii DEDICATION This thesis is dedicated to my wife, Nonhlanhla Mediatrix Nyoni and my daughter, Ilomsa Nicole Nyoni, for their understanding, inspiration, and faithfulness in reminding me that they are my number one team. iv ACKNOWLEDGMENTS This work was only possible with the co-operation of many individuals and institutions. I wish to record my sincere thanks to Prof Titus Msagati and Prof Bhekie Mamba for their supervision and significant academic support throughout my studies. My special appreciation goes to the University of Johannesburg and the Department of Science and Technology/Mintek’s Nanotechnology Innovation Centre for funding this project. I greatly acknowledge Prof Omotayo Arotiba, Prof Sabelo Mhlanga and Dr Edward Nxumalo for their valuable inputs, seminars and professional expertise. I extend my gratitude to Ms Nomsa Baloyi of Extraction Metallurgy for SEM/EDS and X-ray diffraction analysis, Mr Siyasanga Mpelane of Mintek for HRTEM analysis and Dr Petrus Venter, the DWAF: WRM Quality Manager of the Hartbeespoort Dam Integrated Biological Remediation Programme, for willingly helping with sampling and technical aspects of the Hartbeespoort Dam. I also would like to acknowledge my fellow colleagues from the Department of Applied Chemistry: Dr Thabo Nkambule, for helping me with special constructions of the exposure tanks and laboratory staff for creating a warm atmosphere, facilitating interesting discussions and social activities. Mr Njongenhle Nyoni, thank you for endless hours of reading and criticising my thesis - I appreciate your straightforward editing. To my wife Nonhlanhla, how could I ever complete a day’s work without you picking up the slack and organising my schedule? Thank you. I am ever mindful of the unparalleled love, support and patience of my family. Finally, above all things, I would like to acknowledge the only wise God, who has constantly amazed me with His wisdom and divine enablement throughout this work. v PRESENTATIONS AND PUBLICATIONS Conference presentation 1. H. Nyoni, T.A.M. Msagati, B. Mamba. Calibration of a passive, in situ, integrative sampler for monitoring of biotoxins in aquatic environments. 14th WaterNet/WARFSA/GWP-SA Symposium 2013, 30th October -1st November, Dar es salaam, Tanzania, Oral presentation. Publications 1. H. Nyoni, T.A.M. Msagati, B. Mamba. (2014), Calibration of a Passive, in situ, Integrative Sampler for Monitoring of Biotoxins in Aquatic Environments, Water Science & Technology; Water Supply, doi: 10.2166/ws.2015.080 2. Nyoni H, Mamba BB, Msagati TAM (2015) In situ measurement of the time- weighted average concentrations of cylindrospermopsin and microcystin LR-YR- RR in natural waters using silicone-membrane/γ-Fe O -nanoparticle-sorbent 2 3 passive sampling device, J Environ Anal Toxicol, 5: 270. doi: 10.4172/2161- 0525.1000270 3. H. Nyoni, T.A.M. Msagati, B. Mamba. Environmental monitoring of cylindrospermopsin and microcystin LR-YR-RR in the Hartbeespoort dam using a newly developed silicone-membrane/γ-Fe O -nanoparticle-sorbent based 2 3 passive sampler alongside CHEMCATCHER (polar version), POCIS pharmaceutical configuration and SPE technique (grab sampling), (Submitted to Science of the total Environment , February 2015) vi TABLE OF CONTENTS AFFIDAVIT ................................................................................................................................... i ABSTRACT ................................................................................................................................. ii DEDICATION ............................................................................................................................. iv ACKNOWLEDGEMENTS............................................................................................................ v PRESENTATIONS AND PUBLICATIONS .................................................................................. vi Conference presentation ......................................................................................................... vi Publications ............................................................................................................................ vi LIST OF FIGURES AND SCHEMES ............................................................................................. xii LIST OF TABLES .................................................................................................................... xviii LIST OF ABBREVIATIONS ........................................................................................................... xix CHAPTER 1 - INTRODUCTION ..................................................................................................1 1.1 Background ...................................................................................................................1 1.2 Problem statement ........................................................................................................... 3 1.3 Justification of study ......................................................................................................4 1.4 Objectives of the study ..................................................................................................6 1.5 Outline of the thesis ......................................................................................................7 1.6 References ...................................................................................................................8 CHAPTER 2 - LITERATURE REVIEW ......................................................................................... 11 2.1 Environmental concerns of microcystins and cylindrospermopsin ................................ 11 2.2 Instrumental analysis of microcystins and cylindrospermopsin ..................................... 18 2.2.1 High performance liquid chromatography (HPLC) ...................................................... 18 2.2.2 HPLC detectors ......................................................................................................... 20 2.2.3 Gas chromatography (GC) ........................................................................................... 27 2.2.4 Capillary electrophoresis (CE) ................................................................................... 28 2.2.5 Thin layer chromatography (TLC) .............................................................................. 29 2.2.6 Enzyme-Linked Immunosorbent Assay (ELISA)......................................................... 29 2.3 Overview of passive sampling ..................................................................................... 30 2.4 Theory of analyte exchange between passive samplers and water .............................. 39 vii TABLE OF CONTENTS 2.4.1 Equilibrium passive samplers .................................................................................... 42 2.4.2 Kinetic passive samplers ........................................................................................... 42 2.4.3 Environmental factors affecting passive sampler performance ................................... 43 2.4.4 Use of performance reference compounds ................................................................ 45 2.4.5 The use of passive samplers with bioassays ............................................................. 46 2.5 Novelty and theory of the developed passive sampler ................................................. 47 2.6 Alternative techniques to passive samplers ................................................................. 49 2.6.1 Active sampling ......................................................................................................... 49 2.6.2 Bio monitoring organisms .......................................................................................... 50 2.7 Quality Control ............................................................................................................ 51 2.8 References ................................................................................................................. 52 CHAPTER 3 - RESEARCH METHODOLOGY........................................................................... 76 3.1 Materials and methods ................................................................................................ 76 3.1.1 Chemicals and materials ........................................................................................... 76 3.1.2 Microcystin and cylindrospermopsin mixture .............................................................. 77 3.2 Synthesis of iron oxide (maghemite) nanoparticles ...................................................... 77 3.3 Experimental design: flow through exposure system ................................................... 79 3.4 Solid phase extraction technique ................................................................................. 81 3.5 Fabrication of different samplers ................................................................................. 84 3.5.1 Silicone-membrane/γ-Fe O -nanoparticle-sorbent based passive sampler ................. 84 2 3 3.5.2 Polar organic chemical integrative sampler (POCIS) .................................................. 85 3.5.3 Chemcatcher passive sampler ................................................................................... 86 3.6 Chromatographic separation of microcystins ............................................................... 88 3.6.1 High performance liquid chromatography (HPLC) ...................................................... 88 3.6.2 Gas Chromatography – mass spectrometer (GC x GC ToFMS) ................................ 88 3.7 Field evaluation of the passive sampling devices......................................................... 89 3.8 References ................................................................................................................. 91 CHAPTER 4 - CALIBRATION OF A PASSIVE, IN SITU, INTEGRATIVE SAMPLER FOR MONITORING OF BIOTOXINS IN AQUATIC ENVIRONMENTS ................................................ 93 4.1 Introduction ................................................................................................................. 93 viii

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There was no chemical uptake of microcystin compounds into the silicone .. 4.8 Suitability for integrative sampling of control silicone membrane vs.
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