A dissertation submitted to the Faculty of Science, University of the Witwatersrand, Johannesburg, in fulfilment of the requirements for the degree of Masters of Science, 2017 / The tailoring of zeolites surface properties using organic functionalising agents displaying higher binding affinity for metal ions is a widely explored approach for water treatment. In this study, amine functionalised zeolites and phosphate functionalised zeolites were separately synthesised from similar natural zeolite precursors using reflux methods. The surface composition and morphological elucidations were achieved by characterising the adsorbents using Fourier Transform Infra-red spectroscopy (FTIR), thermogravimetric analysis (TGA), Zeta potential, Point of zero charge (pHPZC), and the Brunauer, Emmett and Teller analysis (BET). In case study 5.1, the sorption mechanisms of the uranyl ion onto amine functionalised zeolites (AMZ), activated carbon (AC) and natural zeolite (NZ) were studied as function of various environmental batch parameters. There was effective adsorption when uranium existed as uranyl ions: UO22+ and UO2OH+. The data fitted numerous kinetic and isotherm models suggesting that the equilibrium mechanisms were characteristic of a combination of chemisorption and physisorption for these three adsorbents. The Dubinin-Radushkevich (DR) model did not fit the data and therefore the energy values derived from it were not used to predict the mechanisms involved. However, the thermodynamic evaluations of parameters ∆H, ΔG and ∆S° showed that equilibrium mechanisms were exothermically, randomly and spontaneously favoured for all adsorbents at temperatures ranging between 22 and 40oC. The adsorption capacity of 0.452 mg g-1 was achieved at pH 3 by 500 mg AC dosage using 20 mL volume of 10 mg L-1 uranyl ion solution after equilibrating for 6 h within the temperature ranges of 22 to 30oC. Under the same conditions of sorbent dosage of 500 mg, uranyl solution volume of 20 mL and 10 mg L-1 U(VI) solution concentration, the maximum adsorption capacity of 0.506 mg g-1 for NZ and 0.480 mg g-1 for AMZ were both achieved at pH 4 after equilibration time of 21 h and 6 h with the optimum temperature range of 22 to 30oC, respectively. The model results predict that intraparticle diffusion thorough pores decreased in the order AC ˃ NZ ˃ AMZ while estimating that chemisorption occurred in a reverse order. On the basis of the modelled data, it was deduced that amine functionalisation of natural zeolites improves their chemisorption capability for uranyl ion and can therefore be used as a cost efficient adsorbent for small-scale remediation of contaminated aquatic systems. In another case study 5.2, the surface properties of successfully prepared aminomethyl phosphonic acid functionalised natural zeolite (APZ) were compared to those of commercial silica polyamine composites (SPC) for uranium uptake in batch aqueous solutions. The FTIR spectrum revealed that (3-aminotrimethyl) phosphonic acid functional groups were successfully grafted onto natural zeolite. The TGA analysis showed that the APZ had higher thermal stability and fewer active sites compared to SPC. The optimum adsorption capacity (qe) of 49 mg g-1 and 44 mg g-1 uranium was achieved using 25 mg SPC and 100 mg APZ, respectively at pH 4, 25oC after 1 and 6 h equilibrating time. The data best fitted the pseudo second-order kinetic model and Freundlich isotherm model. The thermodynamic studies showed that adsorption occurred chemically and exothermically for both APZ and SPC. The overall selectivity order for APZ was; Na ˃ Mn ≥ U ˃ Ca ˃ Fe and for SPC was; Fe ˃ Mn ≥ Ca ˃ U˃ Na. The findings showed that phosphate- and amine-functionalised zeolite bind strongly to uranium compared to the unmodified natural zeolite and other conventional adsorbents such as activated carbon. Their selectivity for this element was commendable. With further improvements in the synthetic protocols e.g. by using microwave-based methods, it should be possible to obtain functionalised zeolite that has superior properties to SPC. / XL2017

La voie de signalisation HH joue un rôle crucial dans le contrôle de la prolifération et la différenciation cellulaires. Le dérèglement de cette voie est responsable de nombreux cancers. J’ai ainsi mis en place les outils moléculaires nécessaires pour identifier des régions importantes dans les interactions protéines-protéines au sein du complexe intracellulaire de la voie qui vont permettre de mieux comprendre les mécanismes de régulation du facteur de transcription CI en fonction de l’état d’activation de la voie. Mes travaux ouvrent la voie à de nombreuses études structurales et fonctionnelles de ces protéines jusqu'ici peu étudiées. / The Hedgehog (Hh) signaling pathway is a highly conserved regulator of growth and differentiation that is essential for both vertebrate and invertebrate development. In Drosophila, the HH pathway is regulated by a high molecular weight intracellular protein complex called the Hedgehog Transducing Complex (HTC), whose composition is controlled by the activation of the pathway. My thesis project is to characterise the HTC complex that regulates the fate of the HH transcription factor, CI. I am using structural studies, biochemistry and enzymology to better understand the protein-protein interactions and function that govern the Hedgehog pathway. My work provide a high resolution view of the HTC and help to understand how those proteins work and interact with each other.

Thesis (Master of Engineering in Chemical Engineering)--Cape Peninsula University of Technology, 2019. / A shortage of water has resulted in the need to enhance the quality of wastewater that is released into the environment. The advanced oxidation process (AOP) using heterogeneous catalysis is a promising treatment process for the management of wastewater containing recalcitrant pollutants as compared to conventional processes. As AOP is a reliable wastewater treatment process, it is expected to be a sustainable answer to the shortage of clean water. AOP using heterogeneous catalysis based on Co3O4 particles and PMS, in particular has been found to be a powerful procedure for the degradation and mineralization of recalcitrant organic contaminants. In addition, due to the growing application of Co3O4 in lithium batteries, large quantities of these particles will be recovered as waste from spent lithium batteries, so there is a need to find a use for them. Although this method has received some promising feedback, challenges still need to be addressed, such as the toxicity of cobalt particles, the poor chemical and thermal stability and particle aggregation, and the prompting of lower catalytic efficiency in long haul application. Furthermore, the removal of the catalyst after the treatment of pollutants is also an issue. In order to be applicable, a novel catalyst must be produced requiring the combination of Co3O4 with a support material in order to inhibit cobalt leaching and generate better particle stability. From the available literature, TiO2 was found to be the best support material because it not only provides a large surface area for well dispersed Co3O4, but it also forms strong Co-O-Ti bonds which greatly reduced cobalt leaching as compared to other support materials. Moreover, it also greatly encourages the formation of surface Co–OH complexes, which is considered a crucial step for PMS activation. Therefore, the issues cited above could be avoided by producing a Co3O4/TiO2 heterojunction catalyst.

Chen, Yanmin. / Thesis (Ph.D.)--Chinese University of Hong Kong, 2011. / Includes bibliographical references (leaves 140-160). / Electronic reproduction. Hong Kong : Chinese University of Hong Kong, [2012] System requirements: Adobe Acrobat Reader. Available via World Wide Web. / Abstract also in Chinese.

by Lydia Chang. / Thesis (M.Phil.)--Chinese University of Hong Kong, 1989. / Bibliography: leaves 154-165.

Typescript, etc. / Digitized by Kansas Correctional Industries

Leung, Tsz Yan. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2008. / Includes bibliographical references (leaves 132-146). / Abstracts in English and Chinese. / Acknowledgements --- p.i / Abstract --- p.ii / Table of Contents --- p.vii / List of Figures --- p.xii / List of Plates --- p.xiv / List of Tables --- p.xvii / Abbreviations --- p.xviii / Equations --- p.xxi / Chapter 1. --- Introduction --- p.1 / Chapter 1.1 --- Water crisis and water disinfection --- p.1 / Chapter 1.2 --- Common disinfection methods --- p.2 / Chapter 1.2.1 --- Chlorination --- p.2 / Chapter 1.2.2 --- Ozonation --- p.4 / Chapter 1.2.3 --- Ultraviolet-C (UV-C) irradiation --- p.6 / Chapter 1.2.4 --- Solar disinfection (SODIS) --- p.7 / Chapter 1.2.5 --- Mixed disinfectants --- p.9 / Chapter 1.2.6 --- Other disinfection methods --- p.10 / Chapter 1.3 --- Advanced oxidation processes (AOPs) --- p.11 / Chapter 1.4 --- Photocatalytic oxidation (PCO) --- p.13 / Chapter 1.4.1 --- Understanding of PCO process --- p.15 / Chapter 1.4.2 --- Proposed disinfection mechanism of PCO --- p.18 / Chapter 1.4.3 --- Titanium dioxide (Ti02) photocatalyst --- p.21 / Chapter 1.4.4 --- Irradiation sources --- p.22 / Chapter 1.4.5 --- Bacterial species --- p.23 / Chapter 1.4.5.1 --- Escherichia coli K12 --- p.23 / Chapter 1.4.5.2 --- Shigella sonnei --- p.24 / Chapter 1.4.5.3 --- Alteromonas alvinellae --- p.25 / Chapter 1.4.5.4 --- Photobacterium phosphoreum --- p.26 / Chapter 1.4.6 --- Bacterial defense mechanism towards oxidative stress --- p.27 / Chapter 1.4.6.1 --- Superoxide dismutase (SOD) activity --- p.28 / Chapter 1.4.6.2 --- Catalase (CAT) activity --- p.29 / Chapter 1.4.6.3 --- Fatty acid (FA) profile --- p.30 / Chapter 1.4.7 --- Significance of the project --- p.31 / Chapter 2. --- Objectives --- p.34 / Chapter 3. --- Material and Methods --- p.36 / Chapter 3.1 --- Chemicals --- p.36 / Chapter 3.2 --- Screening of freshwater and marine bacterial culture --- p.36 / Chapter 3.3 --- Photocatalytic reaction --- p.39 / Chapter 3.3.1 --- Preparation of reaction mixture --- p.39 / Chapter 3.3.2 --- Preparation of bacterial culture --- p.39 / Chapter 3.3.3 --- Photocatalytic reactor --- p.41 / Chapter 3.3.4 --- PCO disinfection reaction --- p.42 / Chapter 3.3.4.1 --- Effect of initial pH --- p.44 / Chapter 3.3.4.2 --- Effect of reaction temperature --- p.45 / Chapter 3.3.4.3 --- Effect of growth phases --- p.45 / Chapter 3.4 --- Measurement of superoxide dismutase (SOD) activity --- p.47 / Chapter 3.5 --- Measurement of catalase (CAT) activity --- p.49 / Chapter 3.6 --- Fatty acid (FA) profile --- p.50 / Chapter 3.7 --- Bacterial regrowth test --- p.51 / Chapter 3.8 --- Atomic absorption spectrophotometry (AAS) --- p.52 / Chapter 3.9 --- Total organic carbon (TOC) analysis --- p.53 / Chapter 3.10 --- Chlorination --- p.55 / Chapter 3.11 --- UV-C irradiation --- p.56 / Chapter 3.12 --- Transmission electron microscopy (TEM) --- p.56 / Chapter 4. --- Results --- p.60 / Chapter 4.1 --- Screening of UV-A resistant freshwater and marine bacteria --- p.60 / Chapter 4.2 --- Control experiments --- p.62 / Chapter 4.3 --- Treatment experiments --- p.65 / Chapter 4.3.1 --- UV-A irradiation from lamps --- p.65 / Chapter 4.3.2 --- Fluorescent light from fluorescent lamps --- p.65 / Chapter 4.3.3 --- Effect of initial pH --- p.67 / Chapter 4.3.4 --- Effect of reaction temperature --- p.70 / Chapter 4.3.5 --- Effect of growth phases --- p.70 / Chapter 4.4 --- Factors affecting bacterial sensitivity towards PCO --- p.73 / Chapter 4.4.1 --- Superoxide dismutase (SOD) and catalase (CAT) activities --- p.73 / Chapter 4.4.2 --- Superoxide dismutase (SOD) and catalase (CAT) induction --- p.74 / Chapter 4.4.3 --- Fatty acid (FA) profile --- p.75 / Chapter 4.5 --- Bacterial regrowth test --- p.78 / Chapter 4.6 --- Disinfection mechanisms of fluorescent light-driven photocatalysis --- p.79 / Chapter 4.6.1 --- Atomic absorption spectrophotometry (AAS) --- p.79 / Chapter 4.6.2 --- Total organic carbon (TOC) analysis --- p.81 / Chapter 4.6.3 --- Transmission electron microscopy (TEM) --- p.83 / Chapter 4.7 --- Chlorination --- p.89 / Chapter 4.7.1 --- Disinfection efficiency --- p.89 / Chapter 4.7.2 --- Transmission electron microscopy (TEM) --- p.92 / Chapter 4.8 --- UV-C irradiation --- p.96 / Chapter 4.8.1 --- Disinfection efficiency --- p.96 / Chapter 4.8.2 --- Transmission electron microscopy (TEM) --- p.96 / Chapter 5. --- Discussions --- p.103 / Chapter 5.1 --- Screening of UV-A resistant freshwater and marine bacteria --- p.103 / Chapter 5.2 --- Comparison of PCO coupled with UV-A lamps and fluorescent lamps --- p.103 / Chapter 5.3 --- Effect of initial pH --- p.105 / Chapter 5.4 --- Effect of reaction temperature --- p.106 / Chapter 5.5 --- Effect of growth phases --- p.107 / Chapter 5.6 --- Factors affecting bacterial sensitivity towards PCO --- p.108 / Chapter 5.6.1 --- Superoxide dismutase (SOD) and catalase (CAT) activities --- p.108 / Chapter 5.6.2 --- Superoxide dismutase (SOD) and catalase (CAT) induction --- p.110 / Chapter 5.6.3 --- Fatty acid (FA) profile --- p.110 / Chapter 5.6.4 --- Cell wall structure --- p.112 / Chapter 5.6.5 --- Bacterial size --- p.114 / Chapter 5.6.6 --- Other possible factors --- p.114 / Chapter 5.7 --- Bacterial regrowth test --- p.115 / Chapter 5.8 --- Disinfection mechanisms of fluorescent light-driven photocatalysis --- p.116 / Chapter 5.8.1 --- Atomic absorption spectrophotometry (AAS) --- p.116 / Chapter 5.8.2 --- Total organic carbon (TOC) analysis --- p.117 / Chapter 5.8.3 --- Transmission electron microscopy (TEM) --- p.118 / Chapter 5.9 --- Chlorination --- p.122 / Chapter 5.9.1 --- Disinfection efficiency --- p.122 / Chapter 5.9.2 --- Transmission electron microscopy (TEM) --- p.122 / Chapter 5.10 --- UV-C irradiation --- p.123 / Chapter 5.10.1 --- Disinfection efficiency --- p.123 / Chapter 5.10.2 --- Transmission electron microscopy (TEM) --- p.124 / Chapter 5.11 --- Comparisons of three disinfection methods --- p.124 / Chapter 6. --- Conclusions --- p.126 / Chapter 7. --- References --- p.132

Ho, Sai Man. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2007. / Includes bibliographical references (leaves 144-164). / Abstracts in English and Chinese. / TABLE OF CONTENTS --- p.ii / ABSTRACT --- p.xii / 撮要 --- p.xv / LIST OF ABBREIVIATIONS --- p.xvi / LIST OF TABLES --- p.xvii / LIST OF FIGURES --- p.xix / Chapter Chapter 1 --- General Introduction / Chapter 1.1 --- Overview of lectins --- p.1 / Chapter 1.1.1 --- History of lectins --- p.1 / Chapter 1.1.2 --- Definitions of lectins --- p.2 / Chapter 1.1.3 --- Classification and nomenclature of lectins based on structure --- p.2 / Chapter 1.1.4 --- Classification and nomenclature of lectins based on carbohydrate-bindingspecificity --- p.4 / Chapter 1.1.5 --- Structure of plant lectins --- p.4 / Chapter 1.1.6 --- Biological function of plant lectins --- p.5 / Chapter 1.1.6.1 --- Anti-viral activity of plant lectiins --- p.5 / Chapter 1.1.6.2 --- Lectins as plant defense proteins --- p.6 / Chapter 1.1.6.3 --- Insecticidal activity of plant lectins --- p.7 / Chapter 1.1.6.4 --- Anti-fungal activity of plant lectins --- p.7 / Chapter 1.1.6.5 --- Mitogenic activity of plant lectins --- p.7 / Chapter 1.1.6.6 --- Anti-tumor and anti-proliferative activity of plant lectins --- p.9 / Chapter 1.1.7 --- Background of legume lectins --- p.11 / Chapter 1.1.7.1 --- Structure of legume lectins --- p.11 / Chapter 1.1.7.2 --- Functions and activities of legume lectins --- p.12 / Chapter 1.2 --- Overview of serine protease inhibitors in plants --- p.14 / Chapter 1.2.1 --- Classification of serine protease inhibitor --- p.15 / Chapter 1.2.2 --- The main functions of plant serine protease inhibitors --- p.17 / Chapter 1.2.3 --- Commercial application of serine protease inhibirtors --- p.19 / Chapter 1.2.3.1 --- Medical application --- p.19 / Chapter 1.2.3.2 --- Transgenic application in agriculture --- p.22 / Chapter 1.3 --- Overview of Pathogenesis-related proteins in plants --- p.25 / Chapter 1.3.1 --- Overview of PR-5 family Thaumatin-like proteins (TLPs) --- p.27 / Chapter 1.3.1.1 --- Structural similarities among TLPs --- p.28 / Chapter 1.3.1.2 --- Antifungal activity of TLP --- p.31 / Chapter 1.3.2 --- Overview of Chinase-like proteins (CLPs) --- p.33 / Chapter 1.3.2.1 --- Classification of chitinase --- p.34 / Chapter 1.3.2.1.1 --- On the basis of amino acid sequence of glycosyl hydrolase --- p.34 / Chapter 1.3.2.1.2 --- On the basis of amino acid sequence of plant chitinase --- p.35 / Chapter 1.3.2.2 --- Antifungal activity of CLP --- p.36 / Chapter 1.3.3 --- Anti-freeze property of PR proteins --- p.38 / Chapter 1.3.4 --- Application of PR proteins in agriculture --- p.40 / Chapter 1.4 --- Rationale of the present study --- p.42 / Chapter Chapter 2 --- Materials and Methods / Chapter 2.1 --- Materials --- p.43 / Chapter 2.2 --- Preparation of crude extract --- p.44 / Chapter 2.2.1 --- Hokkaido large black soybean --- p.44 / Chapter 2.2.2 --- Emperor banana --- p.45 / Chapter 2.3 --- Purification --- p.45 / Chapter 2.4 --- Chromatography --- p.46 / Chapter 2.4.1 --- DEAE-cellulose chromatography --- p.46 / Chapter 2.4.2 --- Affi-gel Blue gel --- p.47 / Chapter 2.4.3 --- SP-Sepharse --- p.48 / Chapter 2.4.4 --- Mono Q HR 5/5 and Mono S HR 5/5 --- p.49 / Chapter 2.4.5 --- Superdex 75 and superdex 200 --- p.50 / Chapter 2.5 --- Sodium Dodecyl Sulfate Polyacrylamide Gel Electrophoresis (SDS-PAGE) --- p.50 / Chapter 2.6 --- Protein concentration determination --- p.54 / Chapter 2.7 --- Preparation of rabbit reticulocyte lysate --- p.54 / Chapter 2.8 --- Determination of N-terminal amino acid sequence --- p.56 / Chapter 2.9 --- Assay of inhibition of hemagglutinating activity by different carbohydrates --- p.56 / Chapter 2.10 --- Thermal stability determination assays --- p.57 / Chapter 2.10.1 --- Stability at various temperatures --- p.57 / Chapter 2.10.2 --- Stability at 100°C --- p.57 / Chapter 2.11 --- Assay of pH dependence of hemagglutinating activity --- p.58 / Chapter 2.12 --- Assay of ion dependence of hemagglutinating activity --- p.58 / Chapter 2.13 --- Assay of antifungal activity --- p.58 / Chapter 2.14 --- Assay of trypsin inhibitory activity --- p.60 / Chapter 2.15 --- Assay of antibacterial activity --- p.61 / Chapter 2.16 --- Assay for cytotoxic activity on cancer cell lines --- p.61 / Chapter 2.17 --- Assay for HIV-1 reverse transcriptase (RT) inhibitory activity --- p.62 / Chapter 2.18 --- Assay of mitogenic activity --- p.63 / Chapter Chapter 3 --- Purification and Characterization of Defense-Related Proteins from their Respective Sources / Chapter 3.1 --- Purification and Characterization of a Lectin from the Seeds of Hokkaido large black soybean / Chapter 3.1.1 --- Introduction --- p.65 / Chapter 3.1.2 --- Results --- p.66 / Chapter 3.1.3 --- Purification --- p.68 / Chapter 3.1.3.1 --- Affinity chromatography on Affi-gel Blue gel --- p.69 / Chapter 3.1.3.2 --- Anion-exchange chromatography on DEAE-cellulose --- p.70 / Chapter 3.1.3.3 --- Anion-exchange chromatography on Mono Q column --- p.71 / Chapter 3.1.3.4 --- Gel filtration on Superdex 200 column --- p.72 / Chapter 3.1.3.5 --- Hemagglutinating activity at each purification step --- p.73 / Chapter 3.1.4 --- Characterization of Lectin --- p.74 / Chapter 3.1.4.1 --- Molecular mass determination --- p.74 / Chapter 3.1.4.2 --- N-terminal amino acid sequencing --- p.76 / Chapter 3.1.4.3 --- Assay of inhibition of hemagglutinating activity by different carbohydrates --- p.77 / Chapter 3.1.4.4 --- Thermal stability --- p.78 / Chapter 3.1.4.5 --- Assay of pH dependence of hemagglutinating activity --- p.80 / Chapter 3.1.4.6 --- Assay of ion dependence of hemagglutinating activity --- p.81 / Chapter 3.1.4.7 --- Assay for HIV-1 reverse transcriptase (RT) inhibitory activity --- p.82 / Chapter 3.1.4.8 --- Assay of mitogenic activity --- p.83 / Chapter 3.1.4.9 --- Assay of antibacterial activity --- p.84 / Chapter 3.1.5 --- Discussion --- p.86 / Chapter 3.2 --- Purification and Characterization of a Trypsin inhibitor from the Seeds of Hokkaido large black soybean / Chapter 3.2.1 --- Introduction --- p.93 / Chapter 3.2.2 --- Results --- p.94 / Chapter 3.2.3 --- Purification --- p.95 / Chapter 3.2.3.1 --- Anion-exchange chromatography on Mono Q column --- p.96 / Chapter 3.2.3.2 --- Gel filtration on Superdex 75 column --- p.98 / Chapter 3.2.3.3 --- Trypsin inhibitory activity at each purification step --- p.99 / Chapter 3.2.4 --- Characterization of trypsin inhibitory --- p.100 / Chapter 3.2.4.1 --- Molecular mass determination --- p.100 / Chapter 3.2.4.2 --- N-terminal amino acid sequencing --- p.102 / Chapter 3.2.4.3 --- Assay for HIV-1 reverse transcriptase (RT) inhibitory activity --- p.103 / Chapter 3.2.4.4 --- Antiproliferative effect on MCF-7 and Hep G2 cells --- p.104 / Chapter 3.2.4.5 --- pH and thermal stability --- p.105 / Chapter 3.2.5 --- Discussion --- p.106 / Chapter 3.3 --- Purification and Characterization of a Thaumatin-like protein and Chitinase-like protein from Emperor Banana / Chapter 3.3.1 --- Introduction --- p.108 / Chapter 3.3.2 --- Results --- p.109 / Chapter 3.3.3 --- Purification --- p.111 / Chapter 3.3.3.1 --- Affinity chromatography on Affi-gel Blue gel --- p.112 / Chapter 3.3.3.2 --- Cation exchange chromatography on Mono S column --- p.113 / Chapter 3.3.3.3 --- Gel filtration on Superdex 75 column --- p.114 / Chapter 3.3.3.3.1 --- Fraction MS 2 --- p.114 / Chapter 3.3.3.3.2 --- Fraction MS 4 --- p.115 / Chapter 3.3.3.3.3 --- Fraction MS 5 --- p.118 / Chapter 3.3.4 --- Characterization of the thaumatin-like protein --- p.121 / Chapter 3.3.4.1 --- N-terminal amino acid sequence determination --- p.121 / Chapter 3.3.4.2 --- Assay for antifungal activity --- p.122 / Chapter 3.3.4.3 --- Thermal stability --- p.124 / Chapter 3.3.4.4 --- pH stability --- p.125 / Chapter 3.3.4.5 --- Resistance to trypsin digestion --- p.125 / Chapter 3.3.4.6 --- Anti-HIV-1 reverse transcriptase activity --- p.126 / Chapter 3.3.4.7 --- Discussion --- p.127 / Chapter 3.3.5 --- Characterization of the two chitinase-like protein --- p.131 / Chapter 3.3.5.1 --- N-terminal amino acid sequence determination --- p.131 / Chapter 3.3.5.1.1 --- Emperor banana MS2 CLP --- p.131 / Chapter 3.3.5.1.2 --- Emperor banana MS4 CLP --- p.132 / Chapter 3.3.5.2 --- Assay for antifungal activity --- p.133 / Chapter 3.3.5.3 --- Discussion --- p.136 / Chapter Chapter 4 --- general discussion --- p.138 / References --- p.144

The purpose of the study is to find a suitable method for removal of iron and manganese considering local economic and environmental aspects. El Salvador is situated in Central America with a coast line towards the Pacific Ocean. The country borders Guatemala and Honduras. Aguilares is a town situated in the department of San Salvador, with a population of approximately 33,000 people. Currently, the population is provided with water for about two hours per day, since it is the highest capacity of the existing wells. During these two hours many households fill a small tank with water to use for the remainder of the day. The water is not safe to use for oral consumption because of the levels of bacteria and other contamination. One of the wells, situated in the community of Florída is not in use at this date because of the high levels of Iron and Manganese in the ground water which cannot be removed with the present technique.Ground water is naturally pure from bacteria at a depth of 30 m or more, however solved metals may occur and if the levels are too high the water is unsuitable to drink. The recommended maximum levels by WHO (2008) [1] for Iron and Manganese are 2 mg/l and 0.5 mg/l respectively.Literature and field studies led to the following results; Iron and manganese can be removed by precipitation followed by separation. Precipitation is achieved by aeration, oxygenation or chemical oxidation and separation is achieved by filtration or sedimentation.The different methods all have advantages and disadvantages. However the conclusion reached in this report is that aeration and filtration should be used in the case of Florída. What equipment and construction that should be used depends on economic and resource factors as well as water requirements, which is up to the council of Aguilares to deliberate.

published_or_final_version / Civil Engineering / Doctoral / Doctor of Philosophy