Proton-coupled electron transfer (PCET) is one of the elementary reactions occurring in many chemical and biological systems, such as photosystem II where the oxidation of tyrosine (TyrZ) is coupled to deprotonation of the phenolic proton. This reaction is here modelled by the oxidation of a phenol covalently linked to a Ru(bpy)32+-moitey, which is photo-oxidized by a laser flash-quench method. This model system is unusual as mechanism of PCET is studied in a unimolecular system in water solution. Here we address the question how the nature of the proton accepting base and its hydrogen bond to phenol influence the PCET reaction. In the first part we investigate the effect of an internal hydrogen bond PCET from. Two similar phenols are compared. For both these the proton accepting base is a carboxylate group linked to the phenol on the ortho-position directly or via a methylene group. On the basis of kinetic and thermodynamic arguments it is suggested that the PCET from these occurs via a concerted electron proton transfer (CEP). Moreover, numerical modelling of the kinetic data provides an in-depth analysis of this CEP reaction, including promoting  vibrations  along the O–H–O coordinate that are required to explain the data. The second part describes the study on oxidation of phenol where either water or an external base the proton acceptor. The pH-dependence of the kinetics reveals four mechanistic regions for PCET within the same molecule when water is the base. It is shown that the competition between the mechanisms can be tuned by the strength of the oxidant. Moreover, these studies reveal the conditions that may favour a buffer-assisted PCET over that with deprotonation to water solution.

Esta tesis doctoral está dirigida a la investigación y desarrollo de Procesos de Oxidación Avanzada (POAs), los cuales basan su capacidad en la generación in-situ de radicales hidroxilo (OH·), especie capaz de oxidar muchos compuestos orgánicos. Esta propiedad es aprovechada para conseguir la completa mineralización de los contaminantes o su degradación en sustancias más fácilmente biodegradables.Se plantean dos grandes objetivos:1) Contribuir al conocimiento científico a través del análisis y modelado del proceso UV/H2O2 aplicado a la degradación y mineralización de fenol. Para ello, se ha realizado una planificación experimental dirigida a estudiar la influencia de las variables de operación sobre parámetros globales del proceso, como el contenido total de materia orgánica o la toxicidad.2) Desarrollar una alternativa eficaz para la eliminación de materia orgánica de corrientes residuales de escasa biodegradabilidad mediante la aplicación de POAs. Se ha seleccionado el tratamiento de lixiviados de vertedero de residuos sólidos urbanos (RSU) como caso de estudio y se ha realizado un análisis comparativo de los procesos Fenton y foto-Fenton. Los experimentos se han realizado tanto a escala de laboratorio como a escala de planta piloto. / The aim of this thesis is the research and development of Advanced Oxidation Processes (AOPs). AOPs are based on the in-situ generation of hydroxyl radicals (OH·). These radicals are able to oxidize many organic compounds with high oxidation rates but in a non-selective way. This is useful to achieve the complete mineralization of the pollutants or its degradation into more easily biodegradable compounds.Two main objectives have been pursued in this thesis:1) To contribute to the scientific knowledge of the UV/H2O2 process through its analysis and modelling. Phenol degradation has been selected as a case of study. An experimental planning was established to study the influence of process variables on parameters such as total organic matter concentration and ecotoxicity.2) Research on new alternative treatments for suitable organic matter removal from recalcitrant waste effluents by AOPs. As study case, the leachate remediation from a municipal solid wastes landfill was selected. Fenton and photo-Fenton processes were compared and the operational conditions to achieve the maximum organic matter reduction and colour removal have been determined. Both laboratory scale and pilot plant experiments were carried out.

A bench-scale tubular reactor with recirculation was built in order to study the efficiency of the photocatalytic oxidation of phenol on fluidized titanium oxide-coated silica gel beads. A UV-C lamp placed along the central vertical axes of the reactor was used as source of photons. A bed of silica gel beads was fluidized by means of fluid recirculation and forced to follow upward helical flow around the lamp. Anatase was successfully synthetized on silica gel particles of average diameters 224, 357 and 461 µm, as confirmed by scanning electron micrographs, through a sol-gel technique using a titanium (iv)isopropoxide / hydrochloric acid / ethanol precursor. Data was obtained from multiple 8-hours photocatalytic experiments using a determined mass of beads fluidized in an aqueous solution of known initial phenol concentration. Contaminant degradation with irradiation time was measured as COD. Beads that had been subjected to three consecutive coating procedures produced an 8-h removal efficiency 10% higher than beads with a single coat. 20 g L-1 of silica beads was found to be the optimum load for the experimental reactor configuration regardless of beads size, although efficiency increased with decreasing size of the latter. Experimental results confirmed that the efficiency of phenol photocatalytic degradation decreases with increasing pollutant concentration. Also, the highest removal was achieved with initial pH 3, and it decreased with increasing pH. When NaCl was added to the solution, COD removal increased with increasing salinity. Additionally, it was found that dissolved oxygen is indispensable for photocatalysis to proceed, and that saturation of the treated mixture with oxygen was effectively achieved by keeping the liquid surface in contact with pure oxygen at 1 atm. Finally, statistical analysis of the data showed that photocatalytic mineralization of phenol-derived COD under the experimental conditions follows exponential decay. Based on this finding, a correlation model was proposed for the accurate prediction (minimum R2 = 0.9840) of the COD removal efficiency of the reactor for any given initial COD.