Ces dernières années, de plus en plus de composés organiques réfractaires et toxiques ont été détectés dans les eaux usées. Un bon nombre de ces polluants organiques sont difficilement dégradés par des traitements classiques. Les procédés d’oxydation avancée à base de radicaux sulfates (SR-AOP) sont apparus comme une méthode innovante dans le domaine de la décontamination oxydative des eaux polluées. Des études antérieures ont porté sur ces SR-AOP utilisant du peroxodisulfate (PS) ou du peroxomonosulfate (PMS) comme oxydants, en particulier des couples «métaux de transition et oxydants» (systèmes Fe (II)/PS, systèmes Ni(II)/PMS et Co (II))/PMS), où il a été confirmé que SO4•-·présentent des avantages (sélectivité) par rapport au radical hydroxyle (HO•) pour la décontamination des eaux usées contenant des polluants organiques.Dans cette thèse, nous avons généré des radicaux tels que le radical sulfite SO3•-, le radical sulfate SO4•-, le radical peroxomonosulfate SO5•- à partir d’ions métalliques (Cr(VI), le Co(II), le Fe(III)) capables d’activer le sulfite pour la dégradation des composés organiques. L'efficacité d'élimination et le mécanisme d'oxydation ont été étudiés et le rôle des espèces soufrées a été élucidé. / In recent years, more and more refractory and toxic organic compounds are detected in wastewater. Many of these organic pollutants can hardly be degraded by conventional water treatments. Sulfate radical based advanced oxidation process (SR-AOPs), have emerged as a promising method in the field of oxidative decontamination of polluted water. Past studies focused on this SR-AOPs with peroxydisulfate (PS) or peroxymonosulfate (PMS) as oxidants, especially the ‘transition metal + oxidants’ (i.e. Fe(II)/PS system, Ni(II)/PMS system and Co(II)/PMS system), which has been confirmed that SO4·− has advantages over HO in the decontamination of wastewater containing organic pollutants. In this PhD thesis, oxysulfur radicals including sulfite radical SO3·−, sulfate radical SO4·−, peroxymonosulfate radical SO5·− produced by transition metal ions such as Cr(VI), Co(II), Fe(III) activated sulfite were used to degrade organic compounds. The removal efficiency, the oxidation mechanism were examined, and and the role of sulfur species were elucidated.

Os produtos lácteos são tidos como os alimentos mais perfeitos para o homem devido ao seu alto valor nutritivo. Entretanto, esses produtos vêm refletidos na elevada carga orgânica de efluente gerado. Os Processos Oxidativos Avançados (POA) são métodos químicos baseados na geração de radicais hidroxilas, que promovem a oxidação de compostos orgânicos. O uso de semicondutores no tratamento de efluentes tem sido de grande interesse devido à sua alta eficiência, estabilidade fotoquímica, natureza não-tóxica e baixo custo, especialmente quando a luz do sol é usada como fonte de irradiação. O uso de Óxido de Zinco (ZnO), por exemplo, além de mais econômico, absorve uma fração maior de espectro UV e tem melhor desempenho em pH neutro. Este estudo consistiu em avaliar a aplicação e eficiência da fotocatálise heterogênea (POA) solar com ZnO em termos de percentual de degradação de Carga Orgânica Total (COT) para um posterior tratamento biológico aerado visando melhorar as condições de despejo do efluente de modo a preservar o ecossistema e economia dos recursos naturais. O sistema POA consistiu de um volume fixo de efluente de 3L, de uma chapa metálica 800 x 250 mm revestida com uma formulação de tinta contendo ZnO, um reservatório de vidro, uma bomba centrífuga e aberto para absorção de radiações UV solar. Os resultados foram obtidos e analisados a partir do método de planejamento de experimentos em termos de percentual de degradação de COT. O melhor resultado apresentou um percentual de degradação de COT de 31,5% onde os níves das variáveis estudadas ocorreram em pH 8,0 em chapa de ZnO com espessura de 100 micrômetros (?m), utilizando o efluente in natura e o tempo total de reação de 3 h (180min). O efluente tratado pelo POA solar com ZnO foi submetido ao tratamento biológico aerado. O pH ótimo e a concentração de lodo foram de 6,0 e 5,0 mg/L, respectivamente. O percentual de degradação de COT para os tratamentos combinados foi de 75,1 % para o efluente de laticínios utilizado neste estudo. Isto sugere que o tratamento por POA utilizando ZnO seguido de um Tratamento Biológico Aerado seria uma alternativa promissora no tratamento de efluentes de laticínios. / Dairy products are the most perfect type of food for men due to its high nutritive value reflected on its high organic load of wastewater generated. The Advanced Oxidation Processes (AOP) are chemical methods based on the generation of hydroxyls radicals that promote the oxidation of organic compounds. The use of semiconductors in wastewater treatment has been of great interest owing to its high efficiency, photochemical stability, non-toxic nature and lower costs, especially when sunlight is used as source of irradiation. The use of Zinc Oxide (ZnO), for instance, besides being more economic, it also absorbs a greater range of UV spectrum and it has a better performance on neutral pH. This study consisted in evaluating the application and efficiency of solar photocatalytic oxidation (AOP) with ZnO in percentage terms of removal of Total Organic Carbon (TOC) prior to an aerobic biological treatment aiming to improve the conditions of the disposal of this wastewater in order to conserve the water environment and saving natural resources. The AOP system consisted of a working volume of 3 L, a sheet metal 800 x 250 mm covered with a paint formula containing ZnO, a glass vessel, a pump and an open system in order to collect solar UV radiation. The results were obtained and analyzed from design of experiments in terms of percentage of removal of TOC. The maximum percentage was found to be 31.5 % of removal of TOC and at pH 8.0, thickness of the sheet containing ZnO of 100 micrometers (?m), wastewater in natura and total time of reaction of 3 h (180 min). The solar AOP with ZnO treated wastewater was subjected to an aerobic biological treatment. The optimum pH and sludge loading were of 6.0 and 5.0 mg/L, respectively. The combination of both treatments resulted in 75.1 % of removal of TOC from the dairy wastewater used in this study. This suggests that the AOP using ZnO followed by an aerobic biological treatment would be a promising alternative for the treatment of dairy wastewater.

Neste trabalho buscaram-se formas de aumentar a eficiência do processo de ozonização sobre a degradação/mineralização de corantes empregados pela indústria têxtil, especificamente do azocorante Preto Remazol B, avaliando o emprego do processo de ozonização catalítica tanto homogênea quanto heterogênea. O ozônio mostrou uma grande eficiência para promover a degradação dos três tipos de corantes estudados (azo, antraquinona e ftalocianina); permitindo que soluções destes corantes com concentração de 100 mg L-1 sofressem uma total descoloração (destruição do grupo cromóforo) em menos de 2 minutos de ozonização. Em meio ácido, o ozônio tende a reagir via o mecanismo direto e devido a isto a redução no teor de carbono orgânico total (COT) dos poluentes costuma ser menos eficiente. Em 30 minutos de tratamento o processo O3/pH3 permitiu somente 30% de mineralização do azocorante estudado. Por outro lado, o O3 pode ter sua decomposição catalisada por vários materiais, levando à formação de espécies radicalares, principalmente o radical hidroxila (HO.). Devido ao caráter não seletivo dos radicais hidroxila, o mecanismo de ozonização indireto costuma ser mais eficiente na oxidação de compostos orgânicos. Um exemplo clássico deste mecanismo é o processo O3/pH11, que mineralizou 56% do COT do azocorante após 30 minutos de ozonização. Uma estratégia para promover uma melhora na mineralização do corante Preto Remazol B pelo processo de ozonização em meio ácido foi a adição de peróxido de hidrogênio ao meio reacional. O tratamento O3/pH3/H2O2 permitiu um aumento de 51% na mineralização do azocorante após 30 minutos de ozonização. O aumento da eficiência do ozônio também foi avaliado empregando-se o processo de ozonização na presença de metais (Mn2+e Fe3+). Em 30 minutos de tratamento, o processo O3/pH3/Mn2+ mineralizou 67, 78 e 57% do COT dos corantes Preto Remazol B, Azul Brilhante RN e Turquesa Remazol G, respectivamente. No mesmo tempo de tratamento O3/pH3/Fe3+ permitiu uma remoção de COT de 57, 64 e 41% para Preto Remazol B, Azul Brilhante RN e Turquesa Remazol G, respectivamente. A presença dos metais estudados na forma sólida (MnO2) ou em suportes (SiO2/MnO2 e SiO2/Fe2O3), além de permitir uma remoção de até 79% do COT do azocorante em 30 minutos de tratamento, também mostra uma alternativa para viabilizar o emprego dos agentes catalisadores da decomposição do ozônio, uma vez que na forma suportada os mesmos podem ser utilizados de forma contínua, minimizando etapas de recuperação ou perdas destes materiais. / The main goal of this study was to find means to increase the efficiency of ozonation process over the degradation/mineralization of dyes used in the textile industry, mainly the azodye Remazol Black B, evaluating the use of either homogeneous or heterogeneous catalytic ozonation methods. Ozone showed great efficiency to promote the degradation of the three types of studied dyes (azo, anthraquinone and phtalocyanine) enabling the discoloration (destruction of chromophore group) of solutions with 100 mgdye L-1 in less than 2 minutes. In acidic medium, ozone tends to react via the direct mechanism. In this way, the reduction of total organic carbon (TOC) of the polluents uses to be less efficient. In 30 minutes of treatment, the process O3/pH3 allowed only 30% of mineralization of the studied azodye. On the other hand, O3 can be decomposed by several materials, leading to the formation of radical species, mainly the hydroxyl radical (HO.). Due to the nonselective character of hydroxyl radicals, the indirect mechanism of ozonation usually is more efficient in the oxidation of organic compounds. A classic example of this mechanism is the process O3/pH11 that mineralized 56% of TOC of the azodye after 30 minutes of ozonation. Another strategy to promote an improvement in the mineralization of the azodye Remazol Black B using the ozonation process in acid medium was the addition of hydrogen peroxide to the reactional medium. The treatment O3/pH3/H2O2 enabled an increase of 51% in the mineralization of the azodye after 30 minutes. The increase in the efficiency of ozone was also evaluated using the ozonation process in the presence of metallic ions (Mn2+ and Fe3+). In 30 minutes of treatment, the process O3/pH3/Mn2+ mineralized 67, 78 and 57% of the TOC of the dyes Remazol Black B, Blue Brilliant RN and Remazol Turquoise G133, respectively. In the same time of treatment, the process O3/pH3/Fe3+ mineralized 57, 64 and 41% of the TOC of he dyes Remazol Black B, Blue Brilliant RN and Remazol Turquoise G133, respectively. The presence of the studied metals in the solid form (MnO2) or on supports (SiO2/MnO2 e SiO2/Fe2O3), enabled the removal of up to 79% of the TOC of the azo in 30 minutes of ozonation. Moreover, these methods showed an alternative to permit the use of catalytic agents to decompose ozone, as in the supported form, they can be used in a continuous form, minimizing steps of recuperation or loss of these materials.

A degradação do herbicida Diuron comercial (Nortox SA) foi realizada utilizando os ânodos Ti/RuxTi(1-x)O2 e Ti/IrxTi(1-x)O2 (x = 0,3; 0,5 e 0,7). A investigação da degradação foi conduzida na presença e na ausência de cloreto. O estudo da remoção do herbicida em função da densidade de corrente na ausência de cloreto rendeu remoções de 41 e 49% de demanda química de oxigênio (DQO) e remoções de 10 e 14% de carbono orgânico total (COT) a 100 mA cm-2, respectivamente. Mantendo-se o tempo de eletrólise constante (4 h), a composição do ânodo Ti/Ru0,7Ti0,3O2 foi determinada como a mais ativa para remoção do Diuron e seus subprodutos. Com a adição de cloreto, a taxa de degradação dobrou, e obteve-se 100% de remoção de DQO para o ânodo Ti/Ru0,3Ti0,7O2. O herbicida Alaclor foi totalmente mineralizado por diferentes processos eletroquímicos oxidativos avançados (PEOAs), empregando célula eletroquímica em escala de bancada (100 mL) equipada com cátodo de difusão de ar capaz de eletrogerar H2O2 e ânodos de Pt e diamante dopado com boro (BDD). O melhor desempenho para o tratamento de 100 mL de solução Alaclor 0,60 mmol L-1 durante 360 min, foi obtido por meio do processo fotoeletro-Fenton (FEF) empregando ânodo de BDD na presença de 0,5 mmol L-1 de Fe2+. De acordo com as análises de CG-MS, a etapa de degradação do Alaclor envolveu quatro vias diferentes de reação (desalquilação, ciclização, cisão da ligação R-N e hidroxilação), resultando em nove subprodutos que, em seguida, levaram ao surgimento de ácidos carboxílicos que foram detectados. Diferentes quantidades de íons nitrogenados (NH4+ e NO3-) e clorados (Cl-, ClO3- e ClO4-) foram acumulados nas soluções finais da degradação, dependendo do ânodo e da corrente aplicada. O herbicida Diuron (0,185 mmol L-1 e pH 3,0), foi tratado também por diferentes PEOAs, como oxidação anódica com H2O2 eletrogerado (OA-H2O2), eletro-Fenton (EF) e fotoeletro-Fenton empregando luz UVA (FEF) ou FEF empregando luz solar (FEFS). Os ensaios foram realizados em uma célula eletroquímica em escala de bancada (100 mL) e em seguida testes em uma planta pré-piloto (2,5 L). Nos experimentos com célula eletroquímica em escala de bancada, o tratamento FEF empregando ânodo de BDD foi o método mais potente, produzindo 93% de mineralização após 360 min a 100 mA cm-2. Na planta de fluxo pré-piloto, o processo FEFS atingiu uma porcentagem de mineralização máxima de 70% a 100 mA cm-2. Os ácidos oxálico e oxâmico foram detectados como os ácidos carboxílicos finais e íons amônio e cloreto também foram encontrados, onde o último íon foi parcialmente convertido em íons clorato e perclorato na superfície do ânodo de BDD / Commercial herbicide Diuron solution (Nortox SA) was degrated using Ti/RuxTi(1-x)O2 and Ti/IrxTi(1-x)O2 (x = 0.3, 0.5, and 0.7) anodes. Degradation was investigated in the presence and in the absence of chloride. In the absence of chloride, herbicide removal yielded 41 and 49% COD (chemical oxygen demand) removal, and 10 and 14% TOC (total organic carbon) removal at 100 mA cm-2, respectively. For a constant electrolysis time (4 h), Ti/Ru0.7Ti0.3O2 anode composition removed Diuron and its byproduct the most activelly. Addition of chloride doubled the removal ratio, and the Ti/Ru0.3Ti0.7O2 anode afforded 100% COD removal. Electrochemical advanced oxidation processes (EAOPs) quickly degraded and even totally mineralized the herbicide Alachlor in electrochemical cells equipped with a carbonaceous air-diffusion cathode that was able to electrogenerate H2O2 and with a Pt or boron-doped diamond (BDD) anode. The photoelectron-Fenton (PEF) process with BDD in the presence of 0.5 mmol L-1 Fe2+ performed the best in Alachlor solutions treatment (100 mL, 0.60 mmol L-1, 360 min.). According to GC-MS analyses, Alachlor degradation involved four different reaction pathways (dealkylation, cyclization, R-N bond cleavage and hydroxylation), to give nine byproducts, including the detected carboxylic. Different amounts of nitrogenated (NH4+ and NO3-) and chlorinated (Cl-, ClO3- and ClO4-) ions accumulated in the final solutions depending on the anode and the applied current. The herbicide Diuron (0.185 mmol L-1 and pH 3.0) was treated using different EAOPs like anodic oxidation with electrogenerated H2O2 (AO-H2O2), electro-Fenton (EF), UVA photoelectro-Fenton (PEF), and solar PEF (SPEF). Experiments were performed in 100 mL electrochemical cells, and in a 2.5 L pre-pilot flow plant. In the electrochemical cells, the PEF treatment with BDD was the most potent, yielding 93% mineralization after 360 min at 100 mA cm-2. In the pre-pilot flow plant, the SPEF process furnished maximum mineralization of 70% at 100 mA cm-2. Oxalic and oxamic acids were detected as final carboxylic acids. Ammonium and chloride ions were also released; the latter ion was partially converted into chlorate and perchlorate ions at the BDD surface

La thèse a porté principalement sur la mise en œuvre de procédés d'oxydation avancée permettant l'élimination de trois anti-inflammatoires non stéroïdiens, le kétoprofène, le naproxène et le piroxicam dans l'eau. Ces trois composés sont parmi les médicaments les plus utilisés, dont la présence dans les eaux naturelles présente potentiellement un risque toxicologique. En raison de la faible efficacité d'élimination des produits pharmaceutiques par les stations traditionnels de traitement des eaux usées, les scientifiques se sont mis à la recherche de technologies de traitements efficaces et respectueuses de l'environnement. Les procédés d'oxydation avancée, comme l'ozonation-biofiltration, l'électro-Fenton et l'oxydation anodique peuvent permettre d'atteindre la destruction presque complète des polluants étudiés et de ce fait ils ont suscité un intérêt grandissant au cours des deux dernières décennies. Tout d'abord, ce travail s'intéresse à l'élimination de certains produits pharmaceutiques dans des solutions synthétiques préparées dans l'eau de robinet à l'aide des procédés électro-Fenton et oxydation anodique dans une cellule électrochimique équipée d'une anode de platine ou de diamant dopé au bore et d'une cathode de feutre de carbone. Cette étude a été menée à l'échelle du laboratoire. Les vitesses d'élimination des molécules pharmaceutiques ainsi que le degré de minéralisation des solutions étudiées ont été déterminées sous différentes conditions opératoires. Pendant ce temps, les sous-produits de l'oxidation générés au cours de la minéralisation ont également été identifiés, ce qui nous a permis de proposer les voies d'oxydation possible pour chaque composé pharmaceutique en présence du radical hydroxyl •OH. Enfin, l'évolution de la toxicité au cours des traitements a été suivie en utilisant la méthode Microtox, basée sur l'inhibition de la fluorescence des bactéries Vibrio fischeri. Dans la deuxième partie de ce travail de thèse, les trois anti-inflammatoires non stéroïdiens ont été ajoutés dans une eau déminéralisée ou dans une eau de surface. Ces eaux ont été traitées à l'aide de différentes doses d'ozone; puis le traitement à l'ozone à été combiné à un traitement biologique par biofiltration. Un biofilm biologique déposé à la surface d'un filtre de charbon actif a été utilisé pour déterminer la biodégradabilité des sous-produits d'oxydation formés dans les eaux de surface ozonée. L'identification des intermédiaires formés lors des processus de traitement et des contrôles de toxicité bactérienne ont été menées pour évaluer la voie de dégradation des produits pharmaceutiques et des effets biologiques potentiels, respectivement / 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

Atualmente a classe dos antibióticos se destaca pelo grande consumo e também pelo risco à saúde quando administrado de forma equivocada, esse aumento deve-se ao destaque cada vez maior da indústria de produtos farmacêuticos. Outra questão a ser levantada é a contaminação do meio ambiente por essa classe substâncias, pois após o uso pelo ser humano ocorre a eliminação natural de parte da concentração administrada, assim sendo liberadas nos esgotos e, posteriormente, contaminando os corpos d\'água, a fauna e flora local. Assim, foi proposto um métodos diferente para a degradação desses compostos, utilizando a eletrodos de difusão gasosa (EDG) capazes de gerar peróxido de hidrogênio in situ e em meio ácido, precursores dos radicais hidroxila, responsáveis pela degradação. Foram estudados EDG\'s não catalisados e catalisados, com diferentes porcentagens de ftalocianina de ferro II, com relação à quantidade de peróxido produzido, melhor potencial de produção e cinética do processo. Os resultados revelaram que a incorporação de 0,5% de Ft-Fe no eletrodo apresentou os melhores resultados. Esse eletrodo foi escolhido então para realizar as degradações dos antibióticos sulfametoxazol e trimetoprim. Na célula eletroquímica utilizou-se o processo Fenton, as reações ocorreram em uma faixa de potencial (-0,4 V ≤ E ≤ -1,4 V) e no reator foi utilizado um potencial fixo (-1,75 V) mas utilizando processos de Fenton e Foto-Fenton. As amostras degradadas foram avaliadas por técnicas analíticas de espectroscopia no ultravioleta (UV), cromatografia líquida de alta eficiência (HPLC) e teor de carbono orgânico total (TOC). Os resultados mostraram que, na célula eletroquímica, o melhor potencial de degradação foi de -1,1 V, com uma taxa de redução de 25,5% para o trimetoprim e 96,0% do sulfametoxazol e uma diminuição do teor de carbono orgânico total de 10,4%. Para o reator o melhor resultado foi obtido para o processo de Foto-Fenton onde houve uma redução de 16,9% do teor de carbono orgânico total e uma redução de 99,7% do sulfametoxazol e 11,3% do trimetoprim, em um potencial de -1,75 V. Considerando a formação de subprodutos foi elaborada uma rota de degradação com os possíveis compostos formados. / Currently the class of antibiotics is notable for the large consumption and also the risk to health when administered in error, this increase is due to the growing prominence of the pharmaceutical industry. Another issue to be addressed is the environmental contamination by substances that class, because after use by humans part of the concentration administered is naturally eliminated, thus being released into sewers and subsequently contaminating water bodies, the local fauna and flora. Thus, different methods has been proposed for the degradation of these compounds, using gas diffusion electrodes (GDE) capable of generating hydrogen peroxide in situ and in acid medium, precursors of hydroxyl radicals, responsible for degradation. We studied GDE\'s not catalyzed and catalyzed with different percentages of iron phthalocyanine II, with respect to the amount of peroxide produced better yield potential and kinetic process. The results revealed that the incorporation of 0.5% of Ft-Fe in the electrode showed the best results. This electrode was then chosen to perform the degradation of the antibiotic sulfamethoxazole and trimethoprim. In the electrochemical cell used in the Fenton process, the reactions occurred in a potential range (-0.4 V ≤ E ≤ -1.4 V) and in the reactor was used a fixed potential (-1.75 V) but using Fenton and photo-Fenton processes. Degraded samples were analyzed by analytical techniques, ultraviolet spectroscopy (UV), high performance liquid chromatography (HPLC) and total organic carbon content (TOC). The results showed that in the electrochemical cell, the best degradation potential was -1.1 V, with a reduction rate of 25.5% for trimethoprim and 96.0% for sulfamethoxazole and a decreased carbon content total of 10.4%. For the reactor the best result was obtained for the photo-Fenton process where there was a reduction of 16.9% of the total organic carbon content and a reduction of 99.7% of sulfamethoxazole and 11.3% of trimethoprim, in a potential of -1.75 V. Considering the formation of byproducts was drafted a route with the possible degradation compounds formed.

O efluente lácteo é o resíduo obtido no beneficiamento do leite e seus derivados, sendo considerado um passivo de alto poder poluidor. Sem o devido tratamento, quando lançado nos rios compromete a sobrevivência da biota como um todo. O objetivo deste trabalho consistiu em avaliar a eficiência e aplicação do processo Foto-Fenton, seguido por um tratamento biológico (lodo ativado), para a redução da carga orgânica do efluente em questão. A caracterização do efluente lácteo in natura e tratado foi realizada empregando-se métodos estabelecidos e otimizados [DQO, COT, DBO5, Nitrogênio (orgânico e amoniacal), Fósforo total, Ferro, e Sólidos (ST, STF, STV), fenol, análise de elementos via absorção atômica]. Por meio de planejamentos estatísticos - Taguchi, Box-Behnken e fatorial completo - foram determinados os melhores experimentos posteriores aos tratamentos fotocatalíticos e biológico, tendo como variável resposta a redução percentual de COT. Após o processo fotocatalítico, a amostra do melhor experimento foi tratada por um processo biológico (Sistema Lodo Ativado SLA), a fim de verificar a eficiência de degradação da matéria orgânica do efluente estudado através do sistema conjugado (POA- SLA). O sistema híbrido que apresentou maior eficiência teve como variáveis do processo de tratamento fotoquímico: pH = 3,5; Temperatura = 30 ºC; reagente Fenton ( 35 g H2O2 + 3,6 g Fe2+ ) e potência de radiação ultravioleta de 28 W, para um tempo de reação de 60 minutos. Para o tratamento biológico por lodo ativado, os melhores níveis das variáveis foram realizados em pH = 8 e concentração de lodo de 3,0 g L-1. Os resultados para o tratamento híbrido apresentou percentuais de reduções para COT = 94 %, DQO = 97 % e DBO = 83 %. / The dairy effluent is the residue obtained from the improvement of milk and its derivatives, being considered a high pollutant. Without the due treatment, when thrown in the rivers it puts in risk the survival of the biota as a whole. The objective of this work consisted of evaluating the efficiency and application of the process photo-Fenton followed by a biological (activated sludge) treatment for the reduction of the organic load of the effluent. The characterization of the dairy effluent in natura and treated was accomplished using established methods [COD, TOC, BOD5, Nitrogen (organic and amoniacal), Total Phosphorus, Iron, and Solids (TS, FTS, VTS), phenol, analysis of elements through atomic absorption]. Through statistical designs, Taguchi, Box-Behnken and Full Factorial, the best experiments were determined for the photocatalytic and biological treatments having the reduction of TOC as their response. After the photocatalytic process, the sample of the best experiment was treated by a biological process in order to verify the efficiency of degradation of the organic matter of the effluent studied through the conjugated (AOP - AS) system. The hybrid system that presented larger efficiency had as factors of the photochemical treatment: pH = 3,5, temperature = 30 ºC, Fenton\'s reagent (35g H2O2 + 3,6 g Fe2+) and potency of ultraviolet radiation of 28 W, for 60 minutes of reaction time. As for the biological treatment, it was accomplished in pH = 8 and concentration of sludge of 3g L-1. Obtained were of the hybrid system the percentage of reductions of TOC = 94 %, COD = 97 % and BOD = 83 %.

Du fait du coût élevé de certains matériaux adsorbants d’intérêt pour le traitement de la micropollution organique, l’étude a porté sur la régénération de matériaux adsorbants de type zéolithes hydrophobes et monolithe de carbone dans le cas de l’adsorption du bisphénol A et du diclofénac comme micropolluants réfractaires. Des procédés d’oxydation avancée impliquant des espèces radicalaires HO• (réaction de Fenton, électro-Fenton) et SO₄• – (activation de persulfate par voie thermique) ont été utilisés pour assurer la régénération des matériaux par désorption et dégradation oxydative des polluants fixés. La production de radicaux HO• au sein de la phase aqueuse circulant au niveau de l’adsorbant n’est pas suffisamment efficace pour sa régénération. Il a donc été envisagé de générer les radicaux au plus près des molécules adsorbées. Au cours de ce travail, une méthode sensible d’analyse par polarographie de H₂O₂ a été développée et validée pour le suivi des expériences avec les procédés mettant en jeu la réaction de Fenton. Pour différentes zéolithes, le catalyseur de la réaction de Fenton à base de fer a été incorporé préalablement dans la zéolithe. Pour le monolithe de carbone, les propriétés de conduction du matériau ont été mises à profit en l’utilisant comme cathode pour l’application du procédé électro-Fenton permettant de produire les radicaux HO• directement au sein du matériau. Cela a conduit à améliorer les performances de la régénération avec toutefois une diminution de son efficacité au cours de cycles successifs adsorption/régénération. / The elimination of organic micropollutants often requires the use of adsorption processes among the water treatments. The aim of our study is to regenerate two expensive materials (hydrophobic zeolites and carbon monoliths) to increase their life expectancy and decrease their investing cost. Two organic contaminants were targeted : diclofenac and bisphenol A, which are refractory pollutants. Advanced oxidation processes involve radical species, HO• (Fenton and electro-Fenton reactions) and SO₄• – (thermal activation of persulfate ion). These oxidants were used to decompose the adsorbed pollutants and thus regenerate the adsorbents. The HO• production, within the core of aqueous phase, did not reach satisfactory regeneration, and a loss of adsorption capacity was observed. Furthermore, during this study, a sensitive polarographic analytical method was developed and validated for the quantification of H₂O₂ in the aqueous phase. This method was used to follow in situ the Fenton reaction. The location of the catalyst in a closer vicinity of the adsorbed species was then optimized and the iron catalyst was impregnated in the host, prior to the adsorption, on different types of hydrophobic zeolites. Concerning carbon monolith, the electro-Fenton process was carried out using the material as the cathode thanks to its electrical conductivity. Consequently, HO• are produced in the porosity of monolith. This latter property enhanced the degradation of adsorbed solutes. The overall performances were increased compared to the homogeneous Fenton process. Nonetheless, a decrease of the adsorption capacities with adsorption-regeneration cycles was observed.

Healthcare facility wastewaters are a potentially important and under characterized source of pharmaceuticals and personal care products to the environment. In this study the composition and magnitude of pharmaceuticals and personal care products (PPCPs) released into a single municipality’s wastewater system from a hospital, a nursing care facility, an assisted living facility and an independent living facility are presented for 54 pharmaceuticals, 8 hormones and 31 Alkylphenol ethoxylates (APEOs). Chemical oxidation using molecular ozone and advanced oxidation processes (AOPs) (UV-hydrogen peroxide, Fenton’s Reagent, and Photo – Fenton’s Reagent) were screened and evaluated as potential treatment technologies for removal of APEOs in water and wastewater. In this research, APEOs were found to be dominant PPCP class out of 94 individual analytes measured, accounting for more than 65% of the total mass loading observed leaving the healthcare facility wastewater. Seventy one out of the total measured PPCPs were detected in wastewater from at least one of the facilities. Healthcare facility wastewater are the source of PPCPs to the environment; however, their contribution to the total magnitude of PPCPs in municipal wastewater and the surrounding environment will be determined by the relative flow contribution of wastewater released from the facility to the municipal sewer network. Molecular ozone and advanced oxidation processes were observed to remove APEOs from analyzed water matrices; however, understanding the product formation during the oxidation process is important before concluding a suitable treatment process. Molecular ozone reacted selectively with the double bond in the APEO while AOPs reaction was non selective oxidation. During the AOPs, OH· formation rate and scavenging rate constant of wastewater was found to be the factors governing the oxidation process. Thus, the research carried out informs a risk management decisions concerning the prevalence of PPCPs in the wastewater and use of oxidation systems as a treatment technologies for removal of PPCPs.

This study investigates the rate kinetics for BD and PGMEA oxidation by UV/O3 process. The reactor constructs of a 100 cm x 20 cm x 85 cm (L x W x H) stainless steel chamber, in which four vertical steel plates (20 cm x 65 cm, W x H) were inserted to establish a plug flow path for the flowing gas. The reactor has a total effective volume of 170 L. Each of the five compartments of the reactor is equipped with an individual UV irradiation system with a 3.0-cm x 15-cm (ID x L) quartz sheath that housed an UV lamp, and two electric UV power inputs of 0.147 or 0.294 W/L were obtained. The gas flows perpendicularly to the UV lamps in the reactor. The influent tested VOC concentration was adjusted to about 50 ppm, and the gas flows were controlled at the individual flow rate of 60 and 120 L/min. The effects of moisture content (relative humidity, RH), ozone dosage (initial molar ratio of ozone to the tested VOC, m) and UV volumetric electric power input on the removal of the tested VOCs are investigated in the study. Also, kinetic models of the tested VOCs by photolysis, ozonation and UV/O3 have been developed and confirmed with reference to the experimental data. According to the kinetic models, both photolysis rate and oxidation rate by UV/O3 are following the first order behavior with respect to the tested VOC concentrations which are low. The result reveals the absorbance for the reactions is weak absorbance under UV irradiation. The reaction rates are proportional to the UV electric power inputs in UV-initiated reactions. And the parameter, £i, which represents the ratio of OH radical consumption rate by the tested VOC to the total OH radical consumption rate, can be obtained by simulating the performance of experimental data of OH reactions. The experimental results reveal that for BD oxidation with a gas space time of 85 sec and RH = 40 ¡V 99%, BD photolysis did not occur at wavelength of 185 nm with UV electric power inputs of 0.147 and 0.294 W/L. The ozonation efficiency of BD reached 90% at m = 3.5, and RH had no influence on the removal efficiency of BD. The removal efficiencies by UV/O3 process reached 90% with m = 2.2 and 1.6 for UV power inputs of 0.147 and 0.294 W/L, respectively. The addition of ozone apparently encouraged BD removal efficiency by UV/O3 process. And the enhancement of ozone dosage (m = 0.5 ¡V 4.4) would promote the decomposition of BD more effectively than the enhancements of UV power input (from 0.147 to 0.294 W L-1) and RH (from 40 to 99%). For PGMEA photolysis in a batch reactor with volume of 1.188 L, the photolysis occurred at wavelength of 185 nm under UV irradiation. And the photolysis rate follows the first order behavior with respect to the concentration of PGMEA. But PGMEA photolysis did not occurred at UV wavelength of 254 nm. PGMEA ozonation was performed in the same batch reactor; and the removal efficiency of only 50% at m = 3.96 would take 35 min. So, PGMEA ozonation in the plug flow reactor did not be observed at the conditions of the gas space time of 85 sec and RH = 15 ¡V 99%. Besides, the photolysis of PGMEA was carried out at the above conditions. The removal efficiency of PGMEA by UV/O3 could reach 90% at the conditions of the gas space time of 170 sec, UV volumetric electric power input of 0.294 W/L and m = 2.9. And the enhancement of UV power input (from 0.147 to 0.294 W L-1) would promote the decomposition of PGMEA more effectively than the addition of ozone dosage (m = 1.05 ¡V 15.63) and RH = 15 ¡V 99%.