[ES] En la presente tesis doctoral se ha estudiado la degradación de diferentes mezclas de contaminantes mediante el proceso de oxidación avanzada foto-Fenton solar, buscando alternativas que lo hagan más eficiente a un pH próximo a la neutralidad. Este proceso oxidativo se ha llevado a cabo a pH 5 mediante la adición de sustancias tipo húmicas (STH) extraídas de diferentes residuos orgánicos. Las STH se han extraído del residuo de la producción del aceite de oliva, del residuo del café y de lodos de depuradora deshidratados del reactor anaerobio de EDAR. Estas STH se han caracterizado por diferentes técnicas analíticas y se han adicionado al proceso foto-Fenton para comprobar su eficacia y eficiencia en el mismo. En el caso del uso de las STH provenientes del residuo de la oliva se han obtenido diferentes tiempos de fermentación y diferentes tamaños de fracciones. El estudio sobre STH preparadas sobre residuos con diferentes tiempos de fermentación, demuestra que los mejores resultados de degradación se obtienen con las muestras fermentada un mes, pero en cualquier caso no son significativas las diferencias, por lo que no sería necesario someter al residuo a ningún tiempo de fermentación previo a la extracción de las STH. En los ensayos con diferentes fracciones de STH, se determina que no es necesario el proceso de separación por membranas ya que las degradaciones obtenidas son muy similares, independientemente del uso de una u otra. Se ha probado su eficiencia en diferentes matrices de agua y se ha comprobado su capacidad para complejar el hierro manteniéndolo en disolución, obteniendo buenos resultados en todos los casos. Se han realizado ensayos de toxicidad sobre diferentes organismos para comprobar la detoxificación de las muestras tratadas. Los ensayos de toxicidad determinan que el compuesto clorfenvinfos es el más tóxico y que las muestras en presencia de las STH son más tóxicas antes de aplicar ningún tratamiento, debido a la capacidad surfactante de las mismas. El tratamiento de una mezcla de parabenos con STH de diferente procedencia, mejora los resultados de degradación de contaminantes cuando el proceso se aplica a pH próximo a la neutralidad. Se determina que las STH extraídas del café aplicadas con una cantidad extra de peróxido de hidrógeno (doble de la estequiométrica) proporcionan mejores resultados de degradación de contaminantes que las STH obtenidas de la oliva y del lodo de depuradora. De los ensayos toxicológicos realizados y del de disrupción endocrina, se concluye que el tratamiento durante un t30w de 30 minutos, pese a que consigue la degradación de los parabenos, no resulta suficiente para detoxificar las muestras, ya que las disoluciones finales presentan mayor toxicidad que las intermedias, por lo que se considera prolongar los tratamientos. Las STH extraídas del lodo de depuradora se han utilizado para el lavado de contaminantes cuando se quiere aumentar su concentración y tratar menores volumenes con mayor concentración. Se han acoplado procesos de membrana y procesos oxidativos. Se comprueba que las STH son capaces de atrapar el contaminante por la formación de micelas, impidiendo su paso por la membrana y facilitando el posterior tratamiento por proceso foto-Fenton del retentado obtenido. El análisis realizado por PARAFAC determina que existe una interacción entre las STH y el contaminante. Por otro lado, se ha comprobado la capacidad de generar especies reactivas por parte de las STH en presencia de Fe(II) y Fe(III) obteniéndose una velocidad de reacción más lenta, aunque más estable a lo largo del tiempo con el uso del Fe(III). Las STH extraídas de diferentes residuos han resultado eficientes para la degradación de contaminantes emergentes cuando se lleva el proceso foto-Fenton a pH 5 debido a su capacidad por un lado de complejar el hierro manteniéndolo en disolución y por otro a la capacidad de generar especies reactivas durante el proceso. / [CA] En la present tesi doctoral s'ha estudiat la degradació de diferents mescles de contaminants mitjançant el procés d'oxidació avançada foto-Fenton solar, buscant alternatives que ho facen més eficient a un pH pròxim a la neutralitat. Aquest procés oxidatiu s'ha dut a terme a pH 5 mitjançant l'addició de substàncies tipus húmiques (STH) extragudes de diferents tipus de residus orgànics. Les STH s'han extret del residu de la producció de l'oli d'oliva, del residu del café i de lodes de depuradora deshidratats del reactor anaerobi d'EDAR. S¿han caracteritzat per diferents tècniques analítiques i s'han addicionat al procés foto-Fenton per a comprovar la seua eficàcia i eficiència en el mateix. En el cas de les STH provinents del residu de l'oliva s'han obtingut diferents temps de fermentació i diferents tamanys de fraccions. En l'ús de diferents temps de fermentació millors resultats de degradació s'observen en el cas de la mostra fermentada un mes, però, en qualsevol cas no son significatives les diferències, per el que no és necesari sotmetre al residu a cap temps de fermentació abans de l'extracció. Respecte al assatjos en els diferents tamanys de fraccions es determina que no es necessari la separació per membranes, ja que, les degradacions obtenides son molt similars independentment de l'ús d'una fracció o altra. S'ha comprovat l'efectivitat en diferents matrius d'aigua i la capacitat de les mateixes per a complexar el ferro mantenint-lo en disolució, en bons resultats en tots els casos estudiats. Complementàriament s'han realitzat assajos de toxicitat sobre diferents organismes per tal de comprovar la detoxificació de les mostres tractades. Els assatjos de toxicitat determinen que el compost clorfenvinfos és el més tòxic i que les mostres en presència de les STH són més tòxiques, a causa de la capacitat surfactant d'aquestes. El tractament d'una mescla de parabens en STH de diferent procedència milloren els resultats de degradació de contaminants quan es porta el procés a pH pròxim a la neutralitat. Es determina que les STH extragudes del residu del café quan s'adiciona al procés una quantitat extra de peròxid de hidrògen (doble de la quantitat estequiomètrica) milloren els resultats de degradació de contaminnats comparant en les STH obtingudes de l'oliva i del lodes de depuradora. Dels assatjos toxicològics realitzats i del de disrupció endocrina, es conclou que el tractamnet en una duració de t30w 30 minuts no és suficient per a detoxificar les mostres encara que, la degradació dels parabens es consegueix. Per lo que es considera prolongar el temps de tractament. Les STH procedents del lodes de depuradora s'han utilitzat per al llavat de contaminants quan es troben a concentracions elevades. S'han acoplat processos de membrana i procesos oxidatius. Es comproba que les STH poden atrapar contaminnats per la formació de micel-les, bloquejant el pas del contaminant a través de la membrana i sent més fàcil el posterior tractament per foto-Fenton del retentat obtingut. L'anàlisi realitzat per PARAFAC determina que existeix una interacció entre les STH i el contaminant. D'altra banda, s'ha estudiat el mecanisme de reacció de les STH i la seua capacitat per a generar espècies reactives en presència de Fe(II) i Fe(III), obtinguen una reacció més lenta encara que més estable al llarg del temps en el Fe(III). Les STH extragudes de diferents residus han resultat eficients per a la degradció de contaminants emergents quan es porta el procés foto-Fenton a pH 5 a causa de la seua capacitat per un costat de complexar el ferro mantenint-lo en dissolució i d'altra banda per la seua capacitat de genera espècies reactives durant el procés. / [EN] In the present doctoral thesis, degradation of different pollutant mixtures using the advanced oxidation process called photo-Fenton has been studied, gaining further insight in how this process would take place at circumneutral pHs. Photo-Fenton was carried out at pH 5 by adding humic like substances (HLS) isolated from different organic residues. HLS have been isolated from olive mill wastes, coffee wastes and from wastewater treatment plant sludges. These HLS have been characterized by different analytical techniques and were added to photo-Fenton process to determine their efficacy and efficiency. In the use of HLS isolated from olive mill wastes, different fermentation times and different sizes were obtained. For the HLS from different fermentation times slightly better degradation results were obtained with one month fermentation time, however differences were insignificant to take it into account, and the conclusion of no need of residue fermentation was achieved. In the use of different sizes, the pollutant degradation kinetics were practically the same, concluding that the best option is to use a mixture of them all. Iron complexing ability were studied using different water matrixes with good results in all cases. Toxicity bioassays were carried out using different organisms to know which level of detoxification has achieved. Concluding that these HLS were able to act as iron complexing agents, and that chlorfenvinphos is the most toxic compound, and that water samples containing HLS seems to be more toxic at the end of the treatment time due to their surfactant capacity. A mixture of parabens was treated using different origin HLS at mild photo-Fenton process. HLS isolated from coffee were the most efficient when and extra amount of hydrogen peroxide were added (stoichiometric doble amount). The conclusion reached from toxicology bioassays and endocrine disruption is that the treatment time t30w 30 minutes is not enough to eliminated toxicity, even when the parabens removal was obtained. HLS from sludges were used for contaminant washing when pollutant concentration is high, fitting together membrane system and oxidative process. HLS formed micelles and can catch the pollutant inside, blocking the pass through the membrane. Thus, less volume is treated then by photo-Fenton making easier the process. PARAFAC analysis shows that exist an interaction between HLS and the pollutant. Finally, mechanism reaction between HLS with Fe(II) and Fe(III) and their capacity of generate reactive species were studies. Obtaining that in presence of Fe(III) the reaction is slower but the complex is most stable. HLS isolated from different residue types are useful when photo-Fenton process takes place at circumneutral conditions due to their ability to complex iron, remaining it in solution, and their ability to generate reactive species during the process. Is possible to eliminate emerging pollutants present in wastewaters by photo-Fenton process at mild pH conditions by adding these substances, adding value to the process, and promoting circular economy. / Quiero agradecer al Ministerio de Economía, Industria y Competitividad la concesión de la beca FPI asociada a un proyecto del Plan Nacional de I+D+i (BES- 2016-077962) “Tecnologías eficientes para la eliminación de contaminantes de preocupación emergente, contenidos en Directiva 2013/39/CE o de riesgo significativo según Directiva 2008/105/CE” dentro del que se engloba el trabajo realizado en la presente tesis doctoral. Así como a la Unión Europea por la financiación para la realización de las estancias internacionales. / García Negueroles, P. (2021). Empleo de sustancias tipo húmicas obtenidas a partir de diferentes residuos orgánicos en la eliminación de contaminantes emergentes [Tesis doctoral]. Universitat Politècnica de València. https://doi.org/10.4995/Thesis/10251/177595 / TESIS

Occurrence of organic micropollutants (OMPs) in aquatic environment is a worldwide concern. A long list of anthropogenic substances, including pharmaceuticals, hormones, etc., are frequently detected in natural water sources. Wastewater treatment plants are one main source of OMPs pollution, but also a key step to control OMPs dissemination into the environment. This dissertation focuses on the evaluation of Membrane Aerated Biofilm Reactor (MABR) as a sustainable process to treat wastewater polluted by OMPs. Furthermore, application of high intensity pulsed light is proposed as an innovative tertiary treatment to produce reclaimed water of high quality. In Chapter 1, a literature review was performed to investigate the occurrence and toxicity of 12 selected organic micropollutants (OMPs) in surface and ground water and the limitations of current available biological processes. Among these technologies, systems with enriched nitrifying activity were able to enhance the removal of specific OMPs through cometabolic activities. Thus, I proposed the use of a MABR with enriched nitrifying biomass to treat OMP polluted water. In Chapter 2, I studied the influence of biofilm thickness on the removal of 13 OMPs via MABR. Results demonstrated OMP removal was dependent on biofilm thickness and bacterial cell density. MABR demonstrated important efficiencies in the removal of ammonium, COD, acetaminophen and triclosan at early stages of biofilm thickness. However, the removal of nonpolar, hydrophobic 4 OMPs and anionic, acidic OMPs required thicker biofilms, achieving maximum removal at biofilm with 1.02 mm thickness and 2.2 × 106 cell mL-1. In Chapter 3, the contribution of sorption and biodegradation in the removal of OMPs via MABR was evaluated. At three stages of biofilm thickness studied, biodegradation dominated the removal for most OMPs. Heterotrophs played an important role in OMP biodegradation at all biofilm thickness, while autotrophic nitrifiers enhanced their contribution at thickness beyond 0.58 mm. Increased removal of pollutants like estrone and ethinyl estradiol were linked to the MABR enrichment with nitrifying bacteria. Sorption was essential for the removal of lipophilic and recalcitrant pollutants like triclosan. Finally, to provide high quality treated water for reuse, Chapter 4 explores the use of high-intensity pulsed light (HIPL) as post-treatment. The number of pulses and optical energy dose have a significant impact on the OMPs removal. HIPL demonstrated fast kinetics and efficient photodegradation – with significant OMPs removal within milliseconds. The findings from my Ph.D. dissertation indicate that MABR combined with high-intensity pulse light may be an effective treatment train for the efficient removal OMPs present in municipal wastewaters. This combined treatment process could potentially pave the way to produce high quality reclaimed water for various reuse purposes.

The thesis mainly focused on the implementation of advanced oxidation processes for the elimination of three non-steroidal anti-inflammatory drugs-ketoprofen, naproxen and piroxicam in waters. The three compounds are among the most used medicines, whose presence in waters poses a potential ecotoxicological risk. Due to the low pharmaceuticals removal efficiency of traditional wastwater treatement plants, worldwide concerns and calls are raised for efficient and eco-friendly technologies. Advanced oxidation processes, such as ozonation-biofiltration, electro-Fenton and anodic oxidation processes, which attracted a growing interest over the last two decades, could achieve almost complete destruction of the pollutants studied. Firstly, removal of selected pharmaceuticals from tap water was investigated by electrochemical advanced oxidation processes "electro-Fenton" and "anodic oxidation" with Pt or boron-doped diamond anode and carbon felt cathode at lab-scale. Removal rates and minieralization current efficencies under different operatioanl conditions were analysed. Meanwhile, intermediates produced during the mineralization were also identified, which helps to propose plausible oxidation pathway of each compound in presence of *OH. Finally, the evolution of the global toxicity of treated solutions was monitored using Microtox method, based on the fluorescence inhibition of Vibrio fischeri bacteria. In the second part, the three nonsteroidal anti-inflammatory molecules added in organics-free or surface water were treated under varying ozone treatment regimes with the quite well established technology ozone/biofiltration. A bench-scale biological film was employed to determine the biodegradability of chemical intermediates formed in ozonized surface water. Identification of intermediates formed during the processes and bacterial toxicity monitoring were conducted to assess the pharmaceuticals degradation pathway and potential biological effects, respectively

Les travaux menés au cours de cette thèse ont pour objectif d’étudier l’applicabilité du procédé d’ozonation catalytique TOCCATA® au traitement avancé d’eaux résiduaires urbaines pour le contrôle des émissions en micropolluants. Ce travail couvre la détermination des propriétés physico-chimiques, structurelles et de réactivité de deux catalyseurs et l’optimisation de leur conditionnement pour le procédé d’ozonation catalytique. La caractérisation hydrodynamique du réacteur à co-courant ascendant triphasique en lit fixe utilisé pour la mise en œuvre du procédé a été également réalisée. Les processus élémentaires impliqués dans le procédé ont ensuite été étudiés séparément : transfert gaz-liquide, adsorption, ozonation simple et interaction ozone/matériau. Enfin l’ozonation catalytique a été étudiée vis-à-vis de l’élimination de la matière organique des eaux usées réelles. L’ozonation catalytique se montre moins sélective que l’ozonation simple et améliore le procédé en termes de transfert d’ozone et d’élimination du carbone organique. Des mécanismes et des lois cinétiques pour chacun des processus élémentaires ont été déterminés et une loi de vitesse globale de premier ordre pour le procédé d’ozonation catalytique est proposée. L’étude de l’influence de différentes variables opératoires a été effectuée en vue de l’optimisation du procédé. L’investigation a ensuite été élargie à l’élimination de micropolluants spécifiques (carbamazépine, diuron, kétoprofène, diclofénac, naphtalène) appliquée à des eaux synthétiques, ainsi qu’à des eaux résiduaires urbaines réelles. La plupart des composés sont dégradés après application d’une faible dose d’ozone par le procédé. L’étude de leurs propriétés et de leur affinité avec le système d’ozonation catalytique a permis d’expliquer leurs comportements. / This thesis aimed to study the application of the TOCCATA® catalytic process to urban wastewaters treatment in order to control micropolluant emissions. This work first focused on physico-chemical, structural and reactional properties of two catalysts and on the optimization of their conditioning for the use in the catalytic process. The hydrodynamic characterisation of the fixed bed triphasic co-current upflow reactor used for this study was realized. Elementary processes involved in the process were studied separately: gas-liquid transfer, adsorption, single ozonation, ozone/catalyst interactions. Catalytic ozonation was then investigated for the elimination of organic matter contained in real urban wastewaters. Catalytic ozonation appeared to be less selective than single ozonation and to improve the process in terms of ozone transfer and organic carbon removal efficiency. Mechanisms and kinetic laws were determined for each elementary process and a global first order kinetic law was proposed for catalytic ozonation. The study of various operating conditions (liquid and gas flows, ozone dose …) was conducted in order to optimize the process efficiency.Investigations were then extended towards specific micropollutants elimination (carbamazepine, diuron, ketoprofen, diclofenac, naphtalene) onto synthetic waters as well as real urban wastewaters. Most of the compounds were eliminated with low dose ozonation by the TOCCATA® catalytic ozonation process. The properties of the micropollutants and their affinities with the catalytic ozonation system were studied in order to explain their behaviours.

Os tratamentos convencionais de efluentes em geral não são eficientes para a degradação de compostos persistentes como os fármacos. Neste trabalho, estuda-se o tratamento de soluções aquosas contendo o antibiótico ciprofloxacina (CIP) por meio de processo oxidativo avançado baseado em ozônio. Para tanto, foram realizados experimentos em semi-batelada com recirculação de líquido em um reator (coluna de bolhas) com escoamento gás-líquido em contracorrente. Amostras de líquido foram retiradas e analisadas para medida das concentrações de CIP e de carbono orgânico total (COT); a concentração de ozônio no gás foi medida por espectrofotometria UV-vis. Estudaram-se os efeitos das seguintes variáveis quanto à degradação de CIP, por meio de um planejamento Doehlert: concentração de ozônio à entrada do reator (8-25 mgO3 L-1), pH (3,5-10,5) e concentração inicial de CIP (5-26 mg L-1). Avaliaram-se as seguintes variáveis dependentes por meio da análise de superfícies de resposta: variação de concentração de CIP em 2 minutos; taxa inicial de degradação de CIP e variação de concentração de COT em 30 minutos. Os resultados indicaram total degradação de ciprofloxacina em menos de 15 minutos, tanto por via direta, com ataque por ozônio molecular em meio ácido, como por via indireta, com ataque por radicais hidroxila em meio básico. Os compostos resultantes da degradação da CIP mostraram-se recalcitrantes, obtendo-se maiores remoções de COT após 30 minutos apenas em meio básico ou neutro (máximo de 72,8% para pH=7, [O3]=24,9 mgO3 L-1 e [CIP]0=15,8 mg L-1). Apesar da persistência dos compostos orgânicos remanescentes, os ensaios respirométricos sugeriram que os produtos de degradação são menos tóxicos que o composto de partida, com menor inibição da atividade microbiana. No conjunto, os resultados do trabalho indicam que o processo de ozonização pode ser aplicado para pré-tratamento de efluentes aquosos contendo ciprofloxacina em baixas concentrações, podendo ser associado a processos de tratamento biológico em ETEs antes do descarte. / Conventional wastewater treatment processes are not generally efficient for the degradation of persistent substances like pharmaceutical compounds. In this work, the treatment of aqueous solutions containing the antibiotic ciprofloxacin (CIP) by means of the ozone-based advanced oxidation process is studied. With this aim, experiments were carried out in semi-batch mode with liquid circulation in a bubble column reactor with gas-liquid counter flow. Liquid samples were analyzed for CIP and total organic carbon (TOC) concentrations; ozone concentration in the gas was measured by UVvisible spectrophotometry. The effects of the following variables on CIP degradation were studied according to a Doehlert experimental design: inlet ozone concentration (8 to 25 mgO3 L-1), pH (3.5 to 10.5), initial CIP concentration (5 to 26 mg L-1). The following dependent variables were investigated by response surface analysis: variation in CIP concentration after 2 minutes; CIP initial degradation rate and variation in TOC concentration after 30 minutes. The results showed total degradation of ciprofloxacin in less than 15 minutes either by direct reaction with molecular ozone in acidic medium, or by indirect attack of hydroxyl radicals in alkaline medium. Compounds resulting from CIP degradation showed to be recalcitrant, yielding larger TOC removals after 30 minutes only in alkaline or neutral medium (maximum of 72.8% for pH=7, [O3]=24.9 mgO3 L-1, and [CIP]0=15.8 mg L-1). Despite the persistence of remaining organic compounds, respirometric assays suggested that degradation products are less toxic than the parent compound, exhibiting lower inhibition of microbial activity. Overall, the results indicate that the ozonation process can be used in the pre-treatment of aqueous effluents containing ciprofloxacin in low concentrations, and could be associated with biological treatment processes in wastewater treatment plants prior to final disposal.

Oxidation reactions are of prime importance at an industrial level and correspond to a huge market. Oxidation reactions are widely practiced in industry and are thoroughly studied in academic and industrial laboratories. Achievements in oxidation process resulted in the development of many new selective oxidation processes. Environmental protection also relies mainly on oxidation reactions. Remarkable results obtained in this field contributed to promote the social image of chemistry which gradually changes from being the enemy of nature to becoming its friend and savior. This study dealt with two aspects regarding oxidation process. The first aspect represented an experimental study for the partial oxidation of benzene to phenol using Pd membrane in the gaseous phase. The second part was a theoretical study for some of the advanced oxidation process (AOPs) which are applied for contaminant destructions in polluted waters. Niwa and coworkers reported a one step catalytic process to convert benzene to phenol using Pd membrane. According to their work, this technique will produce a higher yield than current cumene and nitrous oxide based industrial routes to phenol. A similar system to produce phenol from benzene in one step was studied in this work. Results at low conversion of benzene to phenol were obtained with a different selectivity from the reported work. High conversion to phenol was not obtained using the same arrangement as the reported one. High conversion to phenol was obtained using a scheme different from the one reported by Niwa et al1. It was found that producing phenol from benzene is not related to Pd-membrane since phenol was produced by passing all reactants over a Pd catalyst. Within the studied experimental conditions, formation of phenol was related to Pd catalyst since Pt catalyst was not capable of activating benzene to produce phenol. Other evidence was the result of a blank experiment, where no catalyst was used. From this experiment no phenol was produced. A kinetic model for the advanced oxidation process using ultraviolet light and hydrogen peroxide (UV/H2O2) in a completely mixed batch reactor has been tested for the destruction of humic acid in aqueous solutions. Known elementary chemical reactions with the corresponding rate constants were taken from the literature and used in this model. Photochemical reaction parameters of hydrogen peroxide and humic acid were also taken from the literature. Humic acid was assumed to be mainly destroyed by direct photolysis and radicals. The rate constant for the HA- reaction was optimized from range of values in the literature. Other fitted parameters were the rate constant of direct photolysis of hydrogen peroxide and humic acid. A series of reactions were proposed for formation of organic byproducts of humic acid destruction by direct photolysis and radicals. The corresponding rate constants were optimized based on the best fit within the range of available published data. This model doesn't assume the net formation of free radicals species is zero. The model was verified by predicting the degradation of HA and H2O2 for experimental data taken from the literature. The kinetic model predicted the effect of initial HA and H2O2 concentration on the process performance regarding the residual fraction of hydrogen peroxide and nonpurgeable dissolved organic carbon (NPDOC). The kinetic model was used to study the effect of the presence of carbonate/bicarbonate on the rate of degradation of NPDOC using hydrogen peroxide and UV (H2O2/UV) oxidation. Experimental data taken from literature were used to test the kinetic model in the presence of carbonate/bicarbonate at different concentrations. The kinetic model was able to describe the trend of the experimental data. The kinetic model simulations, along with the experimental data for the conditions in this work, showed a retardation effect on the rate of degradation of NPDOC due to the presence of bicarbonate and carbonate. This effect was attributed to the scavenging of the hydroxyl radicals by carbonate and bicarbonate. A kinetic model for the degradation of methyl tert-butyl ether (MTBE) in a batch reactor applying Fenton's reagent (FeII/ H2O2) and Fenton-like reagent (Feo/ H2O2) in aqueous solutions was proposed. All of the rate and equilibrium constants for hydrogen peroxide chemistry in aqueous solutions were taken from the literature. Rate and equilibrium constants for ferric and ferrous ions reactions in this model were taken from the reported values in the literature, except for the rate constant for the reaction of ferric ions with hydrogen peroxide where it was fitted within the range that was reported in the literature. Rate constant for iron dissolution was also a fitted parameter. The mechanism of MTBE degradation by the hydroxyl radicals was proposed based on literature studies. The kinetic model was tested on available experimental data from the literature which involved the use of Fenton's reagent and Fenton-like reagent for MTBE degradation. The degradation of MTBE in Fenton's reagent work was characterized to proceed by two stages, a fast one which involved the reaction of ferrous ions with hydrogen peroxide (FeII/H2O2 stage) and another, relatively, slower stage which involved the reaction of ferric ions with hydrogen peroxide (FeIII/H2O2 stage). The experimental data of MTBE degradation in the FeII/H2O2 stage were not sufficient to validate the model, however the model predictions of MTBE degradation in the FeIII/H2O2 stage was good. Also, the model was able to predict the byproducts formation from MTBE degradation and their degradation especially methyl acetate, and tert-butyl alcohol. The effect of each proposed reaction on MTBE degradation and the byproducts formation and degradation was elucidated based on a sensitivity analysis. The kinetic model predicted the degradation of MTBE for Fenton-like reagent for the tested experimental data. Matlab (R13) was used to solve the set of ordinary nonlinear stiff differential equations that described rate of species concentrations in each advanced oxidation kinetic model. Niwa, S. et al., Science 295 (2002) 105

A presença de antibióticos no meio ambiente aquático tem causado crescente preocupação mundial. Além dos relatos de resistência de bactérias a antibióticos, essa classe de fármacos também pode causar efeitos tóxicos e atuar como perturbadores endócrinos em diversos organismos vivos e, possivelmente, em humanos. Dentre os antibióticos comumente usados destacam-se as sulfonamidas, detectadas em águas subterrâneas e superficiais. Os processos avançados de oxidação (POA) têm sido apontados como tecnologias eficientes para tratamento de poluentes recalcitrantes em diferentes matrizes aquosas. Dentre os POA, o processo foto-Fenton é uma alternativa para a degradação de compostos não biodegradáveis, incluindo fármacos. Uma vez que a principal limitação do processo é o intervalo de pH (2,5- 4,0), a reação pode ser vantajosamente conduzida empregando-se substâncias bio-orgânicas solúveis (BOS) como agentes complexantes de Fe3+ em condições ligeiramente ácidas (pH 5). Por sua vez, o emprego da energia ultrassônica tem sido menos estudado. Nesse contexto, o objetivo deste trabalho é estudar a degradação do antibiótico sulfadiazina (SDZ) por meio do processo foto-Fenton na presença de substâncias bio-orgânicas solúveis (UVvis/ Fe3+/H2O2/BOS) e do processo de cavitação por meio de ultrassom (US). Os resultados obtidos mostram que a sulfadiazina é eficientemente degradada por ultrassom de alta frequência. As maiores porcentagens e taxas de remoção são obtidas usando menor frequência de operação (580 kHz), maior potência dissipada e em pH ligeiramente ácido (melhor condição: pH 5,5). Além disso, a reação de Fenton, combinada com o tratamento US, melhorou notavelmente a degradação da SDZ, particularmente quando quantidades extras de H2O2 foram adicionadas ao sistema. Por sua vez, o uso de BOS como aditivos no processo foto-Fenton apresenta influência marcante na fotodegradação da SDZ em condições ligeiramente ácidas (pH 5). Os BOS podem estabilizar espécies de ferro em solução aquosa em pH próximos ao neutro, o que constitui uma propriedade de grande interesse. Sob as condições estudadas, o BOS CVT230 foi mais eficiente do que FORSUD, provavelmente devido às diferenças nos grupos funcionais presentes na composição destas substâncias. Finalmente, foram calculados os indicadores de consumo de energia elétrica por ordem de grandeza (EEO) para o processo de ultrassom (1572 kW h m-3 ordem-1) e área do coletor por ordem de grandeza (ACO) para o processo foto-Fenton (8,07 m2 m-3 ordem-1). / The potential impacts of antibiotic residues in the environment have become an emerging concern during recent years due to their relation with the development of resistant bacteria, and in some cases to their ability to cause toxic and endocrine disrupting effects in humans and other living organisms. Highlighted among the commonly used antibiotics are the sulfonamides, detected in groundwater and surface water. Advanced oxidation processes (AOP) might constitute an important alternative to deal with pharmaceuticals degradation. Among them, the photo-Fenton process has been widely used. One of its major drawbacks is the highly acidic pH needed (2,5-4,0) to avoid the formation of photochemically inactive iron oxides and hydroxides. The ability of soluble bio-organic substances (SBO) to complex metal cations such as iron is useful for the development of photo-Fenton at mild acidic conditions (pH 5). In turn, the use of ultrasonic energy has been less studied. In this context, the aim of this work is to study the degradation of the antibiotic sulfadiazine (SDZ) by the photo-Fenton process in the presence of soluble bio-organic substances (UV-vis/Fe3+/H2O2/SBO) and by ultrasonic cavitation (US). The results confirm that SDZ is effectively degraded by highfrequency ultrasound. Higher SDZ percent removals and removal rates were observed for the lowest operating frequency (580 kHz), higher dissipated power, and in slightly acidic solution (pH 5.5). On the other hand, SDZ degradation is highly improved in the case of the US/ Fe(II)/H2O2 system. The use of the SBO as Fenton additives in turn has a remarkable influence in SDZ photodegradation at slightly acid conditions (pH 5). This could be ascertained to the complexation of iron by the SBO, hence maintained in the reaction medium as a photoactive species. Under the studied conditions, the BOS CVT230 was more efficient than FORSUD, probably due to differences in the functional groups present in the composition of these substances. Finally, the figures-of merit electrical energy per order (EEO) and collector area per order (ACO) were calculated for the ultrasound (1572 kW h m-3 ordem-1) and photo-Fenton (8,07 m2 m-3 ordem-1) processes respectively.

A new class of treatment processes called Advanced Reduction Processes (ARP) has been proposed. The ARPs combine activation methods and reducing agents to form highly reactive reducing radicals that degrade oxidized contaminants. Batch screening experiments were conducted to identify effective ARP by applying several combinations of activation methods (ultraviolet light, ultrasound, electron beam, microwaves) and reducing agents (dithionite, sulfite, ferrous iron, sulfide) to degradation of five target contaminants (perchlorate, nitrate, perfluorooctanoic acid, 2,4 dichlorophenol, 1,2 dichloroethane) at 3 pH levels (2.4, 7.0, 11.2). These experiments identified the combination of sulfite activated by ultraviolet light produced by a low pressure mercury vapor lamp as an effective ARP. More detailed kinetic experiments were conducted with nitrate and perchlorate as target compounds and nitrate was found to degrade more rapidly than perchlorate. The effects of pH, sulfite concentration, and light intensity on perchlorate and nitrate degradation were investigated. The effectiveness of the sulfite/UV-L treatment process improved with increasing pH for both perchlorate and nitrate.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / In this study, an analytical method was developed for the quantification of statins Atorvastatin and Simvastatin, in hospital effluent (University Hospital of Santa Maria, using Solid phase extraction and Dispersive liquid-liquid microextraction, followed in liquid chromatography coupled to diode array detector. The principal variables of Dispersive liquid-liquid microextraction were investigated with aid of experimental central composite design. The recovery rates of Solid phase extraction varied from 95% for Atorvastatin and 83.2% for Simvastatin, in aqueous solution, and 92.0% for Atorvastatin and 81.5% for Simvastatin, in hospital effluent. As for the Dispersive liquid-liquid microextraction the recovery rates ranged from 85.5% for Atorvastatin and 89.4% for Simvastatin, in aqueous solution, and 83.0% for Atorvastatin and 83.1% for Simvastatin, in hospital effluent. The sampling was carried out in two sample points called Emergency Effluent and General Effluent . The concentration rates detected in the effluent were 30.1 μg L-1 in Emergency Effluent and 29.0 μg L-1 in General Effluent for Atorvastatin and 37.1 μg L-1 in Emergency Effluent and 36.1 μg L-1 in GE for Simvastatin. Ozonation and electrocoagulation were applied for the degradation/removal of statins. The principal variables of electrocoagulation were investigated with aid of experimental central composite design. The degradation rate obtained in ozonation was 100% for Atorvastatin, in 25 minutes reaction for aqueous solution and hospital effluent; and 100% for Simvastatin, in 4 minutes reaction for aqueous solution and 10 minutes reaction in hospital effluent. As for the electrocoagulation the removal rate was 75.6% in aqueous solution and 70.9% in hospital effluent for Atorvastatin; and 100% in aqueous solution and hospital effluent for Simvastatin in 60 minutes reaction. A preliminary risk evaluation revealed that the statins showed a low environmental risk, PEC/PNEC < 1. / Neste trabalho foi desenvolvida metodologia analítica para a quantificação de estatinas Atorvastatina e Sinvastatina, em efluente hospitalar (Hospital Universitário de Santa Maria), utilizando Extração em fase sólida e Microextração dispersiva líquido-líquido seguida de cromatografia líquida com detector de arranjo de diodos. As principais variáveis da Microextração dispersiva líquido-líquido foram investigadas utilizando a Metodologia de Superfície de Resposta através de um delineamento composto central rotacional. As taxas de recuperação da Extração em fase sólida foram de 95,8% para Atorvastatina e 83,5% para Sinvastatina, em solução aquosa e 92,0% para Atorvastatina e 81,5% para Sinvastatina em efluente hospitalar. Já para a Microextração dispersiva líquido-líquido as taxas de recuperação foram de 85,5% para Atorvastatina e 89,4% para Sinvastatina, em solução aquosa e 83,0% para Atorvastatina e 83,1% para Sinvastatina, em efluente hospitalar. A amostragem foi feita em dois pontos de coleta, denominados Efluente PA e Efluente Geral . A concentração média detectada no efluente foi de 30,1 μg L-1 no Efluente PA e 29,0 μg L-1 no Efluente Geral para Atorvastatina e 37,1 μg L-1 no Efluente PA e 36,1 μg L-1 no Efluente Geral para Sinvastatina. Ozonização e eletrocoagulação foram aplicados na degradação/remoção das estatinas. As principais variáveis da eletrocoagulação foram investigadas utilizando a Metodologia de Superfície de Resposta através de um delineamento composto central. As taxas de degradação obtidas na ozonização foram de 100% para Atorvastatina, em 25 min de reação, para solução aquosa e efluente hospitalar; e 100% para Sinvastatina em 4 min em solução aquosa, e 10 min em efluente hospitalar. Já para a eletrocoagulação as taxas de remoção foram de 75,9% em solução aquosa e 70,9% em efluente hospitalar para Atorvastatina; e 100% para solução aquosa e afluente hospitalar para Sinvastatina, em 60 min de reação. A análise preliminar de risco ambiental revelou que as estatinas apresentam baixo risco ambiental, com PEC/PNEC < 1.

Made available in DSpace on 2014-12-17T15:01:16Z (GMT). No. of bitstreams: 1 AndreLNM.pdf: 781178 bytes, checksum: d7b742a561481a98abbefe98cb97f8fb (MD5) Previous issue date: 2005-12-02 / With water pollution increment at the last years, so many progresses in researches about treatment of contaminated waters have been developed. In wastewaters containing highly toxic organic compounds, which the biological treatment cannot be applied, the Advanced Oxidation Processes (AOP) is an alternative for degradation of nonbiodegradable and toxic organic substances, because theses processes are generation of hydroxyl radical based on, a highly reactivate substance, with ability to degradate practically all classes of organic compounds. In general, the AOP request use of special ultraviolet (UV) lamps into the reactors. These lamps present a high electric power demand, consisting one of the largest problems for the application of these processes in industrial scale. This work involves the development of a new photochemistry reactor composed of 12 low cost black light fluorescent lamps (SYLVANIA, black light, 40 W) as UV radiation source. The studied process was the photo-Fenton system, a combination of ferrous ions, hydrogen peroxide, and UV radiation, it has been employed for the degradation of a synthetic wastewater containing phenol as pollutant model, one of the main pollutants in the petroleum industry. Preliminary experiments were carrier on to estimate operational conditions of the reactor, besides the effects of the intensity of radiation source and lamp distribution into the reactor. Samples were collected during the experiments and analyzed for determining to dissolved organic carbon (DOC) content, using a TOC analyzer Shimadzu 5000A. The High Performance Liquid Chromatography (HPLC) was also used for identification of the cathecol and hydroquinone formed during the degradation process of the phenol. The actinometry indicated 9,06&#8901;1018 foton&#8901;s-1 of photons flow, for 12 actived lamps. A factorial experimental design was elaborated which it was possible to evaluate the influence of the reactants concentration (Fe2+ and H2O2) and to determine the most favorable experimental conditions ([Fe2+] = 1,6 mM and [H2O2] = 150,5 mM). It was verified the increase of ferrous ions concentration is favorable to process until reaching a limit when the increase of ferrous ions presents a negative effect. The H2O2 exhibited a positive effect, however, in high concentrations, reaching a maximum ratio degradation. The mathematical modeling of the process was accomplished using the artificial neural network technique / Com o crescente aumento da polui??o das ?guas acorrido nos ?ltimos anos, houve tamb?m um grande avan?o das pesquisas relacionadas ao tratamento de ?guas contaminadas. Efluentes contendo compostos org?nicos de alta toxicidade, nos quais o tratamento biol?gico n?o pode ser aplicado, os chamados processos oxidativos avan?ados (POA) surgem como uma alternativa para a degrada??o de subst?ncias org?nicas t?xicas n?o biodegrad?veis, pois estes processos s?o baseados na gera??o de radicais hidroxila, subst?ncias altamente reativas, capazes de degradar praticamente todas as classes de compostos org?nicos. Os POA, por muitas vezes, requerem o uso de reatores com l?mpadas especiais que emitem luz ultravioleta. Estas l?mpadas apresentam uma alta demanda de energia el?trica, consistindo, portanto, em um dos maiores problemas para a aplica??o desses processos em escala industrial. Este trabalho envolveu o desenvolvimento de um novo reator fotoqu?mico composto de 12 l?mpadas fluorescentes de luz negra de baixo custo como fonte de radia??o UV. O processo estudado foi o sistema foto-Fenton, uma combina??o de ?ons ferrosos, per?xido de hidrog?nio e radia??o ultravioleta, sendo aplicado na degrada??o de um efluente sint?tico aquoso contendo fenol, um dos principais poluentes da ind?stria do petr?leo. Foram realizados experimentos preliminares visando avaliar as condi??es operacionais do reator, al?m dos efeitos da intensidade da fonte de radia??o e distribui??o das l?mpadas no reator. As amostras foram analisadas quanto ao teor de carbono org?nico dissolvido (COD) utilizando um TOC 5000A da Shimadzu. A partir do recurso da cromatografia l?quida de alto desempenho (HPLC), p?de ser identificado a forma??o do catecol e da hidroquinona durante o processo de degrada??o do fenol. Pelo emprego da actinometria foi obtida uma taxa de incid?ncia de f?tons de 9,06&#8901;1018 foton&#8901;s-1, para 12 l?mpadas acionadas. Foi elaborado um planejamento fatorial ampliado do qual foi poss?vel avaliar a influ?ncia da concentra??o dos reagentes (Fe2+ e H2O2), al?m de ter sido determinado as condi??es ?timas experimentais ([Fe2+] = 1,6 mM e [H2O2] = 150,5 mM), obtendo um percentual m?ximo de degrada??o de 81,38 % em 1 hora de rea??o. Foi verificado que o aumento da concentra??o dos ?ons ferrosos ? favor?vel ao processo at? atingir um limite, quando o acr?scimo de ?ons ferrosos come?ou a apresentar um efeito negativo. O H2O2 apresentou um efeito positivo ao processo, atingindo um percentual m?ximo de degrada??o. A modelagem matem?tica do processo foi realizada utilizando o recurso da rede neural artificial, a qual p?de representar o sistema e o comportamento das vari?veis do processo