Multi-electron multi-proton reactions form the basis of nearly every chemical reaction involved in energy storage and manipulation. Despite their importance, the basic properties of these chemical transformations, such as the details of how electron transfer and proton-coupled redox events that must occur during these reactions are controlled, remain poorly understood. The sulfite and nitrite reductase family of enzymes are responsible for carrying out the six-electron reduction of sulfite to sulfide and nitrite to ammonia, respectively. These enzymes play fundamental roles in microbial metabolism and are either dissimilatory or assimilatory in nature. Multi-electron multi-proton reactions are investigated by the study of the catalytic mechanisms of two enzymes that are structurally different, but carry out similarly complex chemistry: the dimeric multi heme cytochrome c nitrite reductase from Shewanella oneidensis and the monomeric siroheme and [4Fe-4S] cluster containing sulfite reductase from Mycobacterium tuberculosis. Employing protein electrochemistry the properties of electron transfer steps and proton-coupled redox steps that occur throughout the catalytic cycle of cytochrome c nitrite reductase during its reduction of substrate revealed the strategies employed by this enzyme. The results presented indicate the reduction of substrate by the enzyme occurs in a series of one electron steps rather than coupled two-electron transfers. Mutational analysis of active site amino acids reveals their role in governing proton coupled redox events, which likely involves a hydrogen bonding network consisting of these residues and water molecules. Additionally, steady state kinetics assays coupled to site-directed mutagenesis of M. tuberculosis sulfite reductase identify a tyrosine residue adjacent to the active site which partially controls substrate preference, by influencing the electronic environment of the active site siroheme cofactor. Stopped-flow absorbance spectroscopy and rapid freeze quench electron paramagnetic resonance studies provide a first glimpse of a potential reaction intermediate during reduction of sulfite by sulfite reductase. Overall, our fundamental understanding of how sulfite and nitrite reductase enzymes catalyze complex multi-electron multi-proton reactions is advanced, and insight into the different approaches Nature employs to govern such powerful chemistry is revealed.

Neste trabalho, 2 diferentes procedimentosforam utilizados para a extração de lignina a partir do licor negro, caracterizando-se quimicamente as amostras de lignina obtidas em relação a umalignina comercial, visando a aplicação no desenvolvimento de sensores voltamétricos. A análise elementar, espectroscopia na região do infravermelho, análise térmica e caracterização eletroquímica do material mostraram que, tanto a origem da lignina quanto a metodologia de obtenção da mesma, a partir do licor negro, podem fornecer materiais com propriedades químicas distintas, embora possuam comportamento eletroquímico similar. Observou-se, também, que a lignina só pode ser armazenada na forma sólida,devido à oxidação pelo oxigênio dissolvidodurante o tempo em que a solução mãe é armazenada.No entanto, a oxidação dalignina é necessária quando se tem por objetivo o desenvolvimento de sensores voltamétricos, devido a predominância de carbonos sp2na estrutura químicaoxidada, condição em que se obtém maior condutividade. Constatou-se também a necessidade de utilizar um transdutor metálico para o desenvolvimento de eletrodos qumicamente modificados com este material, visto que os eletrodos de carbono modificados com lignina oxidada ou não oxidada não apresentaram atividade eletroquímica. Devido à pequena porcentagem de enxofre existente na estrutura química, a lignina oxidada tende a se organizar pelos grupamentos SH quando na presença de ouro, expondo os grupamentos quinônicos eletroativos. A lignina oxidada ainda foi utilizada no preparo de eletrodo de pasta de carbono com nanopartículas de ouro, na qual a lignina oxidada impregnada no grafite atua como redutor \"in-situ\" do ouro, permitindo o preparo de um sensor voltamétrico versátil, capaz de realizar a determinação de ácido ascórbico, dopamina, nitrito e iodato. No que tange ao comportamento eletroquímico de fármacos e estudos de interação fármaco-DNA, eletrodos de carbono foram modificados com DNAdupla fita com a finalidade de monitorar a interação DNA-Gemcitabina.O fármaco não apresentou atividade eletroquímica tanto na região positiva quanto na região negativa de potencial. A interação do mesmo com o DNA promove a condensação/agregação das duplas fitas do DNA em uma primeiraetapa, seguida da clivagem do nucleosídeo guanosina, formando guanina livre. O comportamento eletroquímico de leflunomida e sulfasalazina, dois fármacos aplicados ao tratamento da artrite reumatóide, foi estudado e mecanismos de oxidação foram propostos para cada fármaco. / The chemical properties of samples of lignin, which were precipitated from black liquor using two different methodologies (precipitation with CO2 and H2SO4), were studied and the results compared to those obtained from a commercial lignin sample in order to prepare voltammetric sensors. The elementary analysis, infrared spectroscopy, thermal analysis and electrochemical characterization of the material demonstrated that both, the source of lignin and the precipitation method from the black liquor, can provide lignin samples with different chemical properties, although the electrochemical behavior of all samples has been the same. Lignin could only be stored in solid form as lignin in the black liquor is slowly and quantitatively oxidized by dissolved oxygen, preventing the extraction procedures. However, the lignin as extracted from black liquor cannot be used to modify solid electrodes due its high resistivity. The previous oxidation of the all material was necessary when the aim was its application on the sensors development. The electrical conductivity in the oxidized lignin was achieved, probably due to the predominance of sp2 hybridized carbon atoms, which improved orbital overlapping in the material. In addition, it was necessary to use a metallic transducer to produce electrodes modified with films of lignin with good electrochemical activity. The films drying time was also important parameter, which suggested a specific organization of lignin macromolecules over the electrode surface. Due to the small percentage of sulfur in the material, the oxidized lignin tended to be organized by the SH groups in the presence of metallic substrates, exposing its electroactive quinone groups. The oxidized lignin was further used to prepare carbon paste electrodes modified with gold nanoparticles, in which the impregnated oxidized lignin on graphite acted as an \"in situ\" reducing agent towards HAuCl4.The resulting composite allowed the preparation of a versatile voltammetric sensor, capable of detecting ascorbic acid, dopamine, nitrite and iodate. Regarding the electrochemical behavior and drug interaction studies DNA-molecule, carbon electrodes were modified with double strand DNA with the purpose of monitoring Gemcitabine-DNA interaction. The drug showed no electrochemical activity both, in the positive and the negative potential. The Gemcitabine-DNA interaction promoted condensation / aggregation of the double strand DNA in a first step, followed by cleavage of the nucleoside guanosine in the form of free guanine. In addition, the electrochemical behavior of sulfasalazine and leflunomide, two pharmacological compounds applied to the treatment of rheumathoid arthritis, were studied and their oxidation mechanisms were proposed.

O comportamento eletroquímico da cafeína (CAF) e moléculas análogas, tais como teobromina (TB), teofilina (TF) e xantina (XA), foi estudado utilizando eletrodo de carbono vítreo. Técnicas como voltametria cíclica (VC), voltametria de pulso diferencial (VPD) e onda quadrada (VOQ) e cronoamperometria foram utilizadas para elucidação do mecanismo de oxidação da CAF. Os voltamogramas cíclicos mostraram que todos os compostos estudados apresentaram um único pico irreversível de oxidação na seguinte sequência: Epa(CAF) 1,50V > Epa(TB) 1,34V > Epa(TF) 1,0 V > Epa(XA) 0,74V. Os coeficientes angulares das curvas Ep vs pH foram de 20 mV pH-1, 35 mV pH-1, 58mVpH-1 e 59mVpH-1, respectivamente. A oxidação da TF e XA ocorre envolvendo o mesmo número de elétrons (n) e prótons (H+), enquanto para a cafeína e teobromina, o número de prótons não é igual ao número de elétrons. Este último, foi calculado utilizando os valores de largura de pico à meia altura de corrente dos voltamogramas de pulso diferencial e, exceto a XA, todos os demais derivados foram oxidados em um processo envolvendo 1 elétron. Para a cafeína, o valor de n, coincidiu com aquele calculado pela equação de Randles-Ševcik para sistemas irreversíveis, usando o coeficiente de difusão, D0 = 1,46 x10-5 cm2s-1 e coeficiente de transferência de carga, α, de 0,63. No intervalo de 10 ≤ v ≤ 75mVs-1, os coeficientes angulares dos gráficos (Epa log v) para CAF, TB, TF e XA, foram de 26, 34, 21 mV e 22 mV (década de v)-1, que é o indicativo de um processo de oxidação envolvendo a formação de cátion radical. O número de elétrons determinado por cronoamperometria para a CAF e TB foi n=1 e, comopara TF e XA foram n= 2 e 3,0. Voltamogramas cíclicos e de onda quadrada obtidos em meio de DMSO usando terafluoroborato de tetrabutilamônio mostraram no segundo ciclo, o aparecimento de um par redox quase reversível com E1/2 de + 0,50 V (versus Ag/AgCl), processo atribuído à oxidação do dímero. Para avaliar efeitos de adsorção eletroquímica da CAF na superfície do eletrodo, experimentos de espectroscopia de impedância eletroquímica (EIE) e de potencial de circuito aberto (PCO) foram utilizadas para caracterizar a superfície de eletrodos de carbono vítreo polido (p-ECV), carbono vítreo previamente tratado em solução tampão BR, pH 4,0 (BR-ECV) e carbono vítreo previamente tratado em solução de CAF (CAF-ECV). Os valores de Rct para CAF-ECV foram maiores do que os valores obtidos para o p-ECV, usando solução de K3[Fe(CN)]6 como sonda eletroquímica. / The electrochemical behavior of Caffeine (CAF) and similar molecules such as theobromine (TB), theophylline (TF) and xanthine (XA) was studied using glassy carbon electrode. Techniques such as cyclic voltammetry (CV), differential pulse voltammetry (DPV), square wave voltammetry (VOQ) and chronoamperometry were used to elucidate the CAF oxidation mechanism. Cyclic voltammetry showed that all studied compounds had a single irreversible oxidation peak in the following sequence: Epa (CAF) 1.50V> Epa (TB) 1.34V> Epa (TF) 1.0 V> Epa (XA) 0 .74V. The angular coefficients of Ep versus pH curves were 20, 35, 58 and 59mV/pH, respectively. Oxidation of TF and X occurs involving the same number of electrons (n) and protons (H+), while for caffeine and theobromine, the number of protons is not equal to the number of electrons. The last one was calculated using the peak width values at half-maximum current obtained from the differential pulse voltammograms and, all other derivatives, except for XA, were oxidized in a process involving one electron. For caffeine, the value of n, coincided with that calculated by the Randles-Sevcik equation for irreversible systems, using the diffusion coefficient D0 = 1.46 x10-5 cm2s-1 and the charge transfer coefficient, α, of 0.63. In the range of 10 ≤ v ≤ 75mVs-1, the slopes of the graphs (Epa - log v) to CAF, TB, TF and XA were 26, 34, 21 and 22 mV(v decade)-1, which is indicative of an oxidation process involving the formation of radicalar cation. The number of electrons determined by chronoamperometry for CAF and TB oxidation was n = 1, but for TF and XA were n = 2 and 3.0, respectively. Cyclic and square wave voltammograms obtained in DMSO containing terafluoroborato tetrabutylammonium shown, in the second cycle, a quasi-reversible redox couple almost E1/2 + 0.50 V (vs. Ag / AgCl), attributed to the oxidation of a caffeine dimer. To evaluate the electrochemical adsorption effect of CAF on the electrode surface, electrochemical impedance spectroscopy experiments (IEE) and open circuit potential (OCP) were used to characterize the surface of polished glassy carbon electrodes (p-ECV), glassy carbon previously treated in BR buffer, pH 4.0, (BR-ECV), and glassy carbon previously treated in CAF solution, pH 4,0, (CAF-ECV). The Rct and OCP values for CAF-ECV were larger than the values obtained for p-ECV solution using K3[Fe(CN)6] as the electrochemical probe.

Neste trabalho foi utilizada uma metodologia eletroanalítica para o estudo do comportamento dos pesticidas triazínicos, Atrazina e Ametrina em água e sedimentos do rio Mogi-Guaçu. Para isto utilizou-se a técnica de voltametria de onda quadrada (SWV) e o eletrodo de gota suspensa de mercúrio (HMDE). Inicialmente, os parâmetros experimentais (e voltamétricos) foram otimizados a fim de se obter a melhor resposta, em termos de intensidade de corrente de pico e definição do perfil voltamétrico. As melhores condições encontradas foram: eletrólito suporte CaCl2 0,01 mol L-1 em pH 3,0 e 2,3, para Ametrina e Atrazina, respectivamente, f = 100 s-1; a = 50 mV e DEs=2,0 e 10,0, para Ametrina e Atrazina respectivamente. Após a otimização, curvas de trabalho foram construídas para os dois pesticidas. Foram determinados os limites de detecção (LD) e quantificação (LQ), fatores de recuperação, repetibilidade, reprodutibilidade e sensibilidade da metodologia utilizada. Os resultados obtidos utilizando esta metodologia eletroanalítica foram comparados com os obtidos por HPLC-UV. Para Ametrina e Atrazina em eletrólito preparado com água do Milli-Q, os valores de LD encontrados foram de 2,12 ?g L-1 e 1,16 ?g L-1 e os de LQ foram de 7,06 ?g L-1 e 3,90 ?g L-1, respectivamente. Os valores de LD obtidos utilizando HPLC-UV para Ametrina e para a Atrazina foram de 2,69 ?g L-1 e 1,37 ?g L-1, enquanto aqueles para o LQ foram de 9,01 e 10,62 ?g L-1, respectivamente. Observou-se, desta maneira, que os resultados obtidos usando as duas técnicas são muito próximos e inferiores aos valores recomendados pela Comissão Nacional do Meio Ambiente (CONAMA) para águas residuais e efluentes industriais, 50 ?g L-1 para a Atrazina. Além disto, os valores reportados acima são tão baixos quanto os valores máximos aceitos pela Enviromental Protection Agency (EPA - USA) para águas potáveis, 3 ?g L-1 e pela Agência Nacional de Vigilância Sanitária (ANVISA), também para águas potáveis, 2 ?g L-1. A aplicação da mesma metodologia para águas naturais forneceu parâmetros importantes para verificar o comportamento destes pesticidas em águas, principalmente no que se refere à sua persistência. Foram determinados os limites de detecção (LD) e quantificação (LQ), assim como os fatores de recuperação para amostras de água do Rio Mogi-Guaçu, coletadas em três pontos diferentes, utilizando a técnica de SWV. Para Ametrina em eletrólito preparado com água do rio, os valores de LD variaram entre 15,41 e 29,54 ?g L-1 enquanto que os valores de LQ situaram-se entre 51,38 e 98,49 ?g L-1. Já para a Atrazina, os valores de LD variaram entre 4,90 e 6,19 ?g L-1 e os valores de LQ entre 16,36 e 20,65 ?g L-1 respectivamente. Os fatores de recuperação para Ametrina variaram entre 98,12 e 98,50% e para Atrazina entre 98,00 e 98,80%. As fotodegradações dos pesticidas foram estudadas com a exposição à radiação solar de soluções contendo os pesticidas e preparadas com água do Milli-Q, água de rio e água de rio contendo amostras de sedimentos. Os decaimentos da corrente de pico de redução da Ametrina e da Atrazina com o tempo de exposição à luz solar, variaram conforme o ponto de coleta da água do rio Mogi- Guaçu e a natureza do pesticida. Assim, para a Ametrina as porcentagens de decaimento de corrente após 32 horas de exposição foram de 19,10% (água do Milli-Q); 28,24% (ponto 1); 47,62% (ponto 2) e 30,92% (ponto 3). Já para a Atrazina, as respectivas porcentagens de decaimento das correntes de pico de redução foram de 37,50%; 45,90%; 46,10% e 36,53%. Para soluções contendo os sedimentos, a porcentagem de degradação ficou por volta de 30% para Ametrina enquanto que para a Atrazina a diferença foi marcante, ficando em torno de 86%. Os valores dos coeficientes das isotermas de adsorção de Freundlich obtidos indicaram uma dependência da adsorção com o teor de matéria orgânica e argila no sedimento para os três pontos de coleta do sedimento. De acordo com o critério adotado pelo IBAMA, os pesticidas Ametrina e Atrazina apresentam adsorção baixa, ficando pouco adsorvidos no sedimento. Os valores do 1/n da isoterma de Freundlich variaram entre 1,00 e 1,15 indicando uma característica de partição linear para todos os pontos. Os valores de matéria orgânica para os três pontos de coleta, variaram de 5,45 a 15,16%. A matéria orgânica encontra-se revestindo grande parte das frações minerais do solo e sedimento. Estas frações minerais variam de 15,7 a 20,8%, sendo os teores de silte de 12,3 a 16,3%. / An electroanalytical methodology was employed aiming to study the behaviour of the triazinic pesticides Atrazine and Ametrine in water and sediment collected from the Mogi-Guaçu River. The square wave voltammetry (SWV) and the hanging mercury drop electrode (HMDE) were employed. In a first step, the experimental (and voltammetric) parameters were optimized in order to yield the highest current signals as well as the most well defined voltammetric profiles. The best conditions were achieved as: 0.01 mol L-1 CaCl2 as the support electrolyte at pH 3.0 and 2.3 for Ametrine and Atrazine respectively, f = 100 s-1, a = 50 mV and ?Es = 2.0 and 10.0 for Ametrine and Atrazine respectively. After this initial step, analytical curves were obtained for both pesticides. The corresponding detection (LD) and determination (LQ) limits were calculated, as well as the recovering factors, repeatability, reproducibility and sensibility for the analytical methodology, which was compared with those, obtained using the HPLC-UV. For Ametrine and Atrazine, in pure electrolyte the LD values were 2.12 and 1.16 ?g L-1, while the LQ ones were 7.06 and 3.90 ?g L-1, respectively. The same parameters, obtained with HPLC-UV yielded LD values of 2.69 and 1.37 ?g L-1 for Ametrine and Atrazine, respectively, while the LQ ones were 9.01 and 10.62 ?g L-1, respectively. In this way, it is apparent that the results obtained in this work were very close for both techniques and lower than the minimum limit allowed by the Conselho Nacional do Meio Ambiente (CONAMA) for waste water or industrial effluents, 50 ?g L-1. Moreover, they are close to the maximum allowed value for drinking water postulated by the Environmental Protection Agency (EPA – USA), 3 ?g L-1 and the Agência Nacional de Vigilância Sanitária (ANVISA), 2 ?g L-1. The application of the same methodology for natural water samples yielded important parameters to establish the behaviour of pesticides, mainly concerning with its persistency. It were determined the detection and quantification limits and recovering factors by the SWV technique, for river water samples collected in three different points. For Ametrine, the LD values for electrolytes prepared with river waters, varied between 15.41 and 29.54 ?g L-1, while the values for LQ were between 51.38 and 98.49 ?g L-1. The same values for Atrazine were determined between 4.90 and 6.19 for LD and 16.36 and 20.65 for LQ. The recovering factors for Ametrine were found to be between 91.12 and 98.50% and for Atrazine between 98 and 98.8%. The photodegradations of pesticide molecules were studied by exposition to daylight of solutions containing the pesticides prepared with Milli-Q water, river water and river water containing sediments. The peak current decaying for Ametrine and Atrazine with exposition time varied accordingly the water collection point in the Mogi-Guaçu River and the nature of the pesticide. In this way, for Ametrine the percentage of decaying after 32 hours of exposition were 19.10% for Milli-Q water, 28.24% point 1, 47.62% point 2 and 30.92% point 3. For Atrazine, the respective decaying percentages of peak currents were 37.5%, 45.90%, 46.10% and 36.53% respectively. For solutions containing sediments (also collected in points 1, 2 and 3) the degradation percentage was around 30% for Ametrine, while for Atrazine the difference, around 86%. The coefficients from Freundlich adsorption isotherms presented values depending on the organic matter and clay present in the sediment samples. The pesticides presented low adsorption characteristic on the sediments. The 1/n values from Freundlich isotherm varied between 1.00 and 1.15, indicating a linear partition coefficient characteristic in all points. In this way, it is possible to associate the Kf values with the partition coefficients (Kd). The organic matter content for the three collection points varied between 5.45 and 15.15. The organic matter is found to be covering the mineral fractions of soils and sediments. These mineral fractions varied from 15.7 to 20.8%, while silt content were among 12.3 and 16.3%.

A interação espontânea entre pirita e íons mercúrio foi acompanhada por meio de voltametria cíclica. Eletrodos de carbono grafite e parafina sólida recobertos com grãos de pirita foram mergulhados em soluções contendo íons mercúrio, retirados, lavados e introduzidos na solução de trabalho (solução tampão de ácido acético 0,25M e acetato de sódio 0,25M). Eletrodos que previamente estiveram imersos na solução contendo íons Hg(II) apresentaram um potencial de circuito aberto maior que o potencial típico da pirita na mesma solução. Com o elevado número de novos processos eletroquímicos detectados verifica-se a complexidade do sistema pirita/íons Hg(II) e que mais de uma espécie de mercúrio se deposita espontaneamente sobre o mineral. A possibilidade de formação de sulfeto de mercúrio sobre a pirita foi investigada construindo eletrodos com duas espécies de sulfeto (HgS(preto) e HgS(vermelho)). A resposta eletroquímica do HgS(preto) apresenta processos catódicos e anódicos semelhantes aos processos observados no voltamograma da pirita, após sua interação com íons Hg(II). Entretanto, o perfil eletroquímico do HgS(vermelho) não apresenta qualquer semelhança com voltamograma do sistema pirita/íons Hg(II). Realizou-se estudos para verificar a influência de variáveis químicas (concentração e pH) e físicas (tempo, temperatura e transporte de massa). Observou-se que o transporte de massa acelera o processo de adsorção de espécies de mercúrio sobre a pirita e determinou-se a melhor condição experimental de retirada de íons mercúrio. / The spontaneous interaction between pyrite and mercury ions was studied employing cyclic voltammetry. The electrodes, consisting of solid paraffin and graphite covered by pyrite particles, were immersed in solutions containing mercury ions. After mineral/mercury ions interaction, the electrode was washed and introduced in the working solution (acetic acid 0,25M and acetate of sodium 0,25M). Eletrodes which were immersed in the solution containing mercury ions, presented a open circuit potential more positive than that of the pyrite in the same solution. The high number of new electrochemical processes detected denotes the complexity of the system pyrite/mercury ions and indicates that several species of mercury may deposit spontaneously on the mineral surface. The possibility of formation of mercury sulfide on the pyrite was investigated employing electrodes constructed with HgS(Black) and HgS(red). The electrochemical response of HgS(black) presents cathodic and anodic processes similar to that observed in the voltammogram of pyrite, after interaction with mercury ions. The potentiodynamic profile of HgS(red) it does not present any similarity with the voltammogram of the system pyrite/mercury ions. Studies were carried out to verify the influence of chemical (concentration and pH) and physical variables (time, temperature and mass transport). It was observed that the mass transport accelerates the adsorption process of mercury species on the pyrite surface and the optimal experimental condition for scavenging mercury ions was determined.

Thesis (MTech (Physical Sciences))--Peninsula Technikon, Cape Town, 1999. / Wet deposition of toxic trace metals is the dominant mode of deposition in terrestrial ecosystems and contributes very significantly to their pollution burden. Wet deposited metals are dissolved in rainwater. They reach the vegatation in a form most favourable for uptake. Reliable analysis of toxic trace metals in rainwater is important in order to determine the impact they make on the environment. In this study, trace metals in rainwater and in dry deposition (as a control measure), have been analysed over a period of a year. These metals include cadmium, copper, cobalt, lead, nickel and zinc. The rainwater was filtered, acidified to pH2 and irradiated with UV-light. Dry deposition samples, were digested by heating in nitric acid before analysis. Differential-pulse anodic stripping voltammetry was used to determine cadmium, lead and zinc. Copper was determined by adsorptive cathodic stripping at pH7 after complexation with catechol. Cobalt and nickel were measured at pH9 by adsorptive cathodic stripping after formation of their dimethylglyoximes. Sampling was done on a daily basis from April 1996 to March 1997, on the campus of the Peninsula Technikon. The samples were collected over a 24-hour period. The total average concentration for the metals was 16.11 flg/dm3 for rainwater and 427flg/dm3 for dry deposition. Meteorological factors such as wind speed, humidity and temperature affect the distribution of pollutants and thus the trace metal levels. The levels of the metallic pollutants were thus evaluated against meteorological data. Differential-pulse stripping voltammetry is shown to be applicable for heavy metal analysis of rainwater.

Thesis (MTech (Chemistry))--Peninsula Technikon, Cape Town, 1995 / An analytical method using Differential Pulse Anodic Stripping Voltammetry was developed for determining trace quantities of Cu, Pb, Cd and Zn in airborne particulate matter. The levels of the metallic pollutants were evaluated against meteorological data. Instrumental parameters and sample processing were optimised for determining the metals in the concentration range 1 to 40 μg/l with a percentage relative standard deviation (%RSD) less than 10%. Airborne particulate matter was decomposed by heating in a mixture of Hydrochloric and Sulphuric acids. Recovery studies were used to evaluate the digestion procedure, in the absence of a suitable reference material. The percentage recovery for the metals were between 95% and 100%. A total of 77 air samples were collected from January to December 1992, on the campus of the Peninsula Technikon. The samples were collected over 24 hour periods by filtration at a sampling rate of 20 liters per minute. The total average concentration for the metals was 25.3μg/m³. . No Cd was detected in any of the samples.

The current option for the management of Intermediate-Level Waste (ILW) and High-Level Waste (HLW) in the UK is to store it in stainless steel containers and then placed in a deep underground Geological Disposal Facility (GDF). This may subsequently be backfilled with a cementitious material generating very high pH conditions. The eventual corrosion of the stainless steel canisters containing the waste used for disposal will lead to reducing conditions thereby promoting a low Eh environment. Electrochemical experiments are needed to determine which uranium species is/are present at a particular pH and to model the redox behaviour of aqueous uranium in a potential GDF. The main aim of this project is to use cyclic voltammetry to deduce peak potentials for the various uranium redox couples in aqueous solution across the pH range and in particular the hyperalkaline range, as the surroundings of a GDF will be in high pH conditions. Data in the literature have been obtained only under acidic conditions where they were subsequently extrapolated to obtain data for alkaline conditions in some reports. Is this valid however? Experiments are therefore needed to obtain fundamental data under alkaline conditions to fill in gaps in the literature. In addition to radionuclides, complexing organic ligands present in a cementitious repository could have an important effect on the immobilisation of radionuclides in concrete. This is due to the ability of the ligands to form complexes with cations, thereby enhancing their solubility and mobility in the cement pore water. Four different ligands were investigated in this project that are relevant to nuclear waste disposal which comprised of carbonate, ethylenediaminetetraacetic acid (EDTA), gluconic acid and α-isosaccharinic acid (α-ISA). The peak potentials of each uranium redox reaction in aqueous solution were measured and the potentials were compared in ligand and non-ligand systems. The voltammograms were compared to obtain their similarities and differences in terms of the shape of the cyclic voltammograms, peak potentials, reversibility, current responses and etc. Analysis of the similarities and differences was needed to be able to increase the understanding of the complexation effects of these ligands with uranium under different pH conditions in aqueous solution.

No description available.

Electrochemical and spectroelectrochemical techniques were employed to investigate the redox characteristics of dyes for dye sensitized solar cells (DSCs) adsorbed at the surface of fluorine-doped tin oxide (FTO) and FTO TiO2 electrodes. In this work are studied Ru-based dyes such as cis-bis(isothiocyanato)-bis(2,2’-bipyridyl- 4,4’dicarboxylato)-ruthenium(II) (N719) and (cis-RuLL'(SCN)2 with L=4,4'- dicarboxylic acid-2,2'-bipyridine and L'=4,4'-dinonyl-2,2'-bipyridine) known as Z907, and indoline organic dyes coded as D102, D131, D149, and D205. The adsorption, diffusion and stability of adsorbed dyes were studied using cyclic voltammetry in acetonitrile and 0.1 M NBu4PF6. The adsorption technique at FTO electrodes was optimized in order to be reproducible so that electrochemical studies as a function of dye coverage were carried out. Langmuirian binding constants were approximately estimated for all dyes adsorbed at FTO electrodes. Rate constants for the chemical degradation of the oxidized dye were also obtained. Is shown that degradation of the dyes mainly occurs at the surface of FTO and only insignificant degradation is evident once the dyes are adsorbed on TiO2. The degradation of dye adsorbed on FTO is shown to affect charge transport from the nonporous TiO2 via electron hopping. Spectroelectrochemical studies of indoline dyes adsorbed on FTO/TiO2 electrodes revealed a red shift of absorption peaks after oxidation and the presence of a strong charge transfer band in the near IR that suggest delocalization of holes in the dye layer. This is consistent with observation that the diffusion coefficient for hole conduction in the adsorbed dye layer is several orders of magnitude higher for the organic dyes compared to the Ru-based dyes. DSCs fabricated using indoline dyes showed good performance. Incident photon-tocurrent conversion efficiency (IPCE) spectra and I-V characteristics are presented.