Ultraviolet direct photolysis (UV) and the advanced oxidation process UV/H2O2 are new technologies in the water treatment industry. Both treatments can cause the transformation of organic compounds. Nitrosamines and organic chloramines are disinfection by-products (DBPs) formed from the reaction of organic nitrogen compounds during chlorination or chloramination (chlor(am)ination) disinfection. It is therefore possible for UV and UV/H2O2 to affect the organic compound precursors for nitrosamines and organic chloramines and thus their formation from subsequent chlor(am)ination. The precursor compounds, UV and H2O2 doses used for UV or UV/H2O2, and alkalinity were found to have an effect on the formation of nitrosamines and organic chloramines during bench-scale experiments. Full scale studies found UV and UV/H2O2 had different effects on the formation of different nitrosamine species and organic chloramine concentrations, and that a potential correlation existed between the formation of organic chloramines from chlorination and the formation of N-nitrosodimethylamine from chloramination.

Ultraviolet direct photolysis (UV) and the advanced oxidation process UV/H2O2 are new technologies in the water treatment industry. Both treatments can cause the transformation of organic compounds. Nitrosamines and organic chloramines are disinfection by-products (DBPs) formed from the reaction of organic nitrogen compounds during chlorination or chloramination (chlor(am)ination) disinfection. It is therefore possible for UV and UV/H2O2 to affect the organic compound precursors for nitrosamines and organic chloramines and thus their formation from subsequent chlor(am)ination. The precursor compounds, UV and H2O2 doses used for UV or UV/H2O2, and alkalinity were found to have an effect on the formation of nitrosamines and organic chloramines during bench-scale experiments. Full scale studies found UV and UV/H2O2 had different effects on the formation of different nitrosamine species and organic chloramine concentrations, and that a potential correlation existed between the formation of organic chloramines from chlorination and the formation of N-nitrosodimethylamine from chloramination.

Biological and physical chemistry treatment methods always are used to remove COD of organic wastewater contains PCB. The effect is not obvious when the compositions of pollutant are too refractory or complicated. The primary treatment method of wastewater containing copper is chemical coagulation/sedimentation and its disadvantage is producing a large of sludge. The objective of this study, using two combinative method of UV/H2O2-Ferrite Process and Fenton-Ferrite Process, is to remove organic compounds and heavy metal in real wastewater. Not only supernatant liquid could meet the standard of discharge wastewater but also produce general(non-hazardous) industrial wastes of heavy metal. The primary operation condition of Fenton and UV/H2O2 process, was ferrous ion and hydrogen peroxide concentration, pH, reaction time, and chemical dosing, searching best operation condition to combine with Ferrite Process. Operation of Fenton and UV/H2O2 process under acid condition (pH=2) and neutral condition (pH=8) showed the best operation condition of Fenton and UV/H2O2. The removal decreased when the dose of hydrogen peroxide was added too more or too less. As Fenton and UV/H2O2 process test finished, Ferrite Process is next used for treatment of heavy metal wastewater; Ferrite Process conducted as three stages and the operation conditions were controlled with temperature, pH and the ratio of Fe/M mole. The results showed that the best removal of treatment of copper containing wastewater by Ferrite Process achieved when the ratio of Fe/M mole was at 10. Treatment of PCB industrial real wastewater by Fenton-Ferrite Process and UV/H2O2-Ferrite Process which combined with Fenton, UV/H2O2 and Ferrite Process. The supernatant liquid containing organic compounds and heavy metal both could meet the standards of discharge wastewater and the sludge was judged with general(non-hazardous) wastes. The characteristic of the sludge were the diameter lattice less 100 nm and with magnetism and to develop recovery and utilization in a further work.

This study was to investigate the treatment of paraquat-containing solutions by advanced oxidation processes (denoted by AOPs). The operation parameters conducted in semi-batch reactor were as follows: the effect of ozone dose, pH and H2O2 concentration on conversion of paraquat by adding O3, UV, O3/H2O2, UV/H2O2 and UV/O3/H2O2. Paraquat concentration: 10 ppm and 20 ppm, ozone dose: 45 g/hr and 105 g/hr, and H2O2 concentration: 0,07 g/l, 0.71 g/l and 1.127 g/l were tested. In the first stage of pre-test, the purpose was to observe the decomposition of paraquat under various pH in order to compare the conversions by O3 and by O2, and to select the optimal pH in above AOPs. The performances of AOPs for treating paraquat-containing solutions were found in sequence as follows: O3/H2O2, O3, UV/O3, UV/H2O2/O3, UV/H2O2 and UV. The process of O3/H2O2 not only could remove higher concentration of paraquat but also had to need a shorter residence time. The effect of parameters on the removal of paraquat by each AOPs were discussed. The kinetics of AOPs in treatment of paraquat-containing solutions was confirmed by using half-life test. Except UV and UV/H2O2 processes nearing zero order, the apparent reaction order of O3, UV/O3, UV/O3/H2O2 and O3/H2O2 were obtained to be one. Based on the removal and cost analysis, O3/H2O2 (O3 = 45 g/hr, H2O2 dose = 0.71 g/l) was the best process in treating paraquat solutions for the low energy and economic cost. As for the O3 and UV/O3 processes, we also recommended to be yours truly options.

Os efluentes corados ainda são um problema em estações de tratamento de esgoto. Os corantes normalmente apresentam estruturas complexas e difíceis de serem degradadas por processos convencionais, entrando no meio ambiente aquático e causando impacto visual, mudanças nas características físico-químicas da água, prejudicam a fotossíntese do meio e podem apresentar efeitos ecotóxicos. Para o tratamento de vários tipos de efluentes, os Processos Oxidativos Avançados (POAs) são eficientes, rápidos e promovem uma oxidação não seletiva. Os POAs podem se tornar mais eficazes com o acoplamento de outras tecnologias, como as micro-ondas. As micro-ondas não possuem energia suficiente para quebrar as ligações intermoleculares, mas quando somadas ao processo UV/H2O2 pode haver um efeito sinérgico melhorando o desempenho do POA. Neste trabalho, buscou-se a otimização do processo UV/H2O2 acoplado às micro-ondas utilizando-se uma lâmpada de descarga sem eletrodo (LDE) de Hg e Fe. Utilizou-se um planejamento experimental para estudar a degradação de uma mistura de três corantes ácidos de classes diferentes: Acid Blue 9 (C.I. 42090, triarilmetano), Acid Red 92 (C.I. 45410, xanteno) e Acid Yellow 23 (C.I. 19140, monoazo). A variável-resposta observada foi a concentração residual dos corantes medida por CLAE. As condições ótimas para o tratamento foram: concentração inicial de peróxido de hidrogênio = 125 mg L-1, pH= 6,2 e vazão = 800 mL min-1. Em 180 min de tratamento, correspondente a 45 min de irradiação alcançou-se uma degradação de 23, 20 e 98% para AB9, AR92 e AY23 respectivamente. O modelo cinético foi de pseudo 1ª ordem para o AY23, com k = (1,7 ±0,041) × 10-2 min-1 e R² = 0,990. Não foi possível determinar a cinética de degradação do AB9 e do AR92 por causa da baixa degradação alcançada (aproximadamente uma ordem de grandeza menor). A partir das análises de espectrometria de massas, observou-se um único produto de degradação: o AY23 monohidroxilado. Esse produto não apresentou ecotoxicidade para o organismo-teste L. sativa. No entanto, ele foi tóxico para o organismo D. similis, imobilizando os microcrustáceos em todas as diluições testadas. / Colored effluents are still a problem in wastewater treatment plants. Dyes usually have complex structures that are difficult to be degraded by conventional processes, thus entering into the aquatic environment and causing visual impact, changes in the water physicochemical characteristics, impairing photosynthesis, and posing ecotoxic effects. For the treatment of various types of wastewater, the Advanced Oxidation Processes (AOP) are efficient, fast and promote non-selective oxidation. AOPs can become more effective by coupling them to other technologies, such as microwaves. Microwaves do not have enough energy to break intermolecular bonds, but when coupled to the UV/H2O2 process, there may be a synergistic effect improving the AOP performance. In this study, the UV/H2O2 process coupled to microwaves, using an Hg and Fe electrodeless discharge lamp (EDL), was optimized. An experimental design was performed to study the degradation of a mixture of three acid dyes of different classes: Acid Blue 9 (C.I. 42090 , triarylmethane), Acid Red 92 (C.I. 45410, xanthene), and Acid Yellow 23 (C.I. 19140, monoazo). The observed response variable was the residual concentration of the dyes measured by HPLC. The optimum conditions for the treatment were: initial hydrogen peroxide concentration = 125 mg L- 1, pH = 6.2, and flow rate = 800 mL min-1. In 180 min of treatment, corresponding to 45 min of irradiation, it was achieved a degradation of 23, 20, and 98% for AB9, AR92, and AY23 respectively. The AY23 degradation followed a pseudo-first-order kinetic model, with k = (1.7 ±0,041) × 10-2 min-1 and R² = 0.990. It was not possible to determine the degradation kinetics of AB9 and AR92 due to the low degradation achieved (approximately one order of magnitude lower). From mass espectrometry analyses, only one degradation product was observed: monohydroxilated AY23. That product showed no ecotoxicity towards the test-organism L. sativa. However, it was toxic towards the test-organism D. similis, immobilizing the microcrustaceans in all tested dilutions.

Os efluentes corados ainda são um problema em estações de tratamento de esgoto. Os corantes normalmente apresentam estruturas complexas e difíceis de serem degradadas por processos convencionais, entrando no meio ambiente aquático e causando impacto visual, mudanças nas características físico-químicas da água, prejudicam a fotossíntese do meio e podem apresentar efeitos ecotóxicos. Para o tratamento de vários tipos de efluentes, os Processos Oxidativos Avançados (POAs) são eficientes, rápidos e promovem uma oxidação não seletiva. Os POAs podem se tornar mais eficazes com o acoplamento de outras tecnologias, como as micro-ondas. As micro-ondas não possuem energia suficiente para quebrar as ligações intermoleculares, mas quando somadas ao processo UV/H2O2 pode haver um efeito sinérgico melhorando o desempenho do POA. Neste trabalho, buscou-se a otimização do processo UV/H2O2 acoplado às micro-ondas utilizando-se uma lâmpada de descarga sem eletrodo (LDE) de Hg e Fe. Utilizou-se um planejamento experimental para estudar a degradação de uma mistura de três corantes ácidos de classes diferentes: Acid Blue 9 (C.I. 42090, triarilmetano), Acid Red 92 (C.I. 45410, xanteno) e Acid Yellow 23 (C.I. 19140, monoazo). A variável-resposta observada foi a concentração residual dos corantes medida por CLAE. As condições ótimas para o tratamento foram: concentração inicial de peróxido de hidrogênio = 125 mg L-1, pH= 6,2 e vazão = 800 mL min-1. Em 180 min de tratamento, correspondente a 45 min de irradiação alcançou-se uma degradação de 23, 20 e 98% para AB9, AR92 e AY23 respectivamente. O modelo cinético foi de pseudo 1ª ordem para o AY23, com k = (1,7 ±0,041) × 10-2 min-1 e R² = 0,990. Não foi possível determinar a cinética de degradação do AB9 e do AR92 por causa da baixa degradação alcançada (aproximadamente uma ordem de grandeza menor). A partir das análises de espectrometria de massas, observou-se um único produto de degradação: o AY23 monohidroxilado. Esse produto não apresentou ecotoxicidade para o organismo-teste L. sativa. No entanto, ele foi tóxico para o organismo D. similis, imobilizando os microcrustáceos em todas as diluições testadas. / Colored effluents are still a problem in wastewater treatment plants. Dyes usually have complex structures that are difficult to be degraded by conventional processes, thus entering into the aquatic environment and causing visual impact, changes in the water physicochemical characteristics, impairing photosynthesis, and posing ecotoxic effects. For the treatment of various types of wastewater, the Advanced Oxidation Processes (AOP) are efficient, fast and promote non-selective oxidation. AOPs can become more effective by coupling them to other technologies, such as microwaves. Microwaves do not have enough energy to break intermolecular bonds, but when coupled to the UV/H2O2 process, there may be a synergistic effect improving the AOP performance. In this study, the UV/H2O2 process coupled to microwaves, using an Hg and Fe electrodeless discharge lamp (EDL), was optimized. An experimental design was performed to study the degradation of a mixture of three acid dyes of different classes: Acid Blue 9 (C.I. 42090 , triarylmethane), Acid Red 92 (C.I. 45410, xanthene), and Acid Yellow 23 (C.I. 19140, monoazo). The observed response variable was the residual concentration of the dyes measured by HPLC. The optimum conditions for the treatment were: initial hydrogen peroxide concentration = 125 mg L- 1, pH = 6.2, and flow rate = 800 mL min-1. In 180 min of treatment, corresponding to 45 min of irradiation, it was achieved a degradation of 23, 20, and 98% for AB9, AR92, and AY23 respectively. The AY23 degradation followed a pseudo-first-order kinetic model, with k = (1.7 ±0,041) × 10-2 min-1 and R² = 0.990. It was not possible to determine the degradation kinetics of AB9 and AR92 due to the low degradation achieved (approximately one order of magnitude lower). From mass espectrometry analyses, only one degradation product was observed: monohydroxilated AY23. That product showed no ecotoxicity towards the test-organism L. sativa. However, it was toxic towards the test-organism D. similis, immobilizing the microcrustaceans in all tested dilutions.

Os processos oxidativos avançados são promissores para a degradação de compostos orgânicos resistentes aos tratamentos convencionais, como o fenol. A fluidodinâmica computacional (CFD) tornou-se uma poderosa ferramenta para analisar processos fotoquímicos por resolver os balanços acoplados de quantidade de movimento, de massa e de radiação. O objetivo deste trabalho é investigar o processo UV/H2O2 num reator fotoquímico anular usando CFD e um modelo cinético mais realista. O modelo em CFD foi criado de forma progressiva. Inicialmente, foram determinados os campos de velocidade para três vazões (30, 60 e 100 L/h). Considerou-se dois diâmetros de lâmpada para reproduzir a configuração experimental do sistema. A discretização foi feita com malhas tetraédricas variando entre 390 000 e 1 200 000 elementos. Quatro modelos de turbulência RANS foram analisados: k-e, k-w, o shear stress transport (SST) e o modelo de tensões de Reynolds (RSM). O campo de velocidades foi validado comparando a DTR com seu levantamento experimental. A próxima etapa foi incluir o mecanismo de degradação de fenol proposto por Edalatmanesh, Dhib e Mehrvar (2008) no modelo em CFD. Trata-se de um modelo cinético baseado em equações dinâmicas para todas as espécies. O campo de radiação foi calculado pelo modelo radial e pela solução da equação de transporte de radiação através do método discrete transfer. As simulações reproduziram dados experimentais abrangendo uma larga gama de concentrações iniciais de fenol, razões molares H2O2/fenol e três potências de emissão das lâmpadas. O campo de velocidades obtido era dependente da vazão: o fluido pode manter movimento helicoidal sobre toda a extensão do reator ou se desenvolver como um escoamento pistonado. O modelo k-e não reproduziu bem o escoamento por não ser adequado para escoamentos rotativos. Os outros modelos geraram curvas de DTR com bom ajuste aos dados experimentais, especialmente o modelo k-w. O desvio médio entre as simulações de degradação de fenol e os dados experimentais é inferior a 8%. Verificou-se que, devido ao escoamento rotativo, os reagentes ficavam concentrados próximos à parede externa e migravam para a região da lâmpada ao longo do reator. A elevada intensidade de radiação na superfície da lâmpada criou uma camada ao seu redor na qual a fotólise do H2O2 ocorreu com grande taxa. Os radicais OH gerados nessa camada eram transportados para a região das paredes por convecção. Isso fez com que a maior parte do fenol fosse atacada na segunda metade do reator e gerou acúmulo do radical próximo à lâmpada na seção de saída do reator, já que o poluente já fora oxidado nessa área. O método discrete transfer previu intensidades de radiação maiores que o modelo radial, e, consequentemente, maior concentração de radicais OH. Os resultados satisfatórios indicam que CFD foi uma ferramenta adequada para analisar este escoamento reativo. / Advanced oxidation processes are a promising technology for degradation of organic compounds resistant to conventional treatments such as phenol. Computational fluid dynamics (CFD) has recently emerged as a powerful tool that allows a deeper understanding of photochemical processes in reactor engineering by solving the coupled momentum, mass and radiation balances. This work aimed to investigate the UV/H2O2 process in an annular photoreactor using CFD and a more realistic kinetic model. A progressive approach was used to develop the CFD reactor model. First, the velocity fields were determined for three volumetric flow rates (30, 60 and 100 L/h). Two lamp diameters were considered to reflect the experimental configuration of the system. Tetrahedral meshes varying form 390,000 to 1,200,000 elements were analyzed to achieve grid independence. For accounting turbulence effects, four RANS models were tested: k-e, k-w, the Shear Stress Transport (SST) and the Reynolds Stress models (RSM). The velocity field was validated through comparison to RTD experimental data. Next step was introducing the mechanism of phenol degradation proposed by Edalatmanesh, Dhib and Mehrvar (2008) into the CFD model. This kinetic model is based on dynamic equations for all species. The fluence rate field was calculated by the radial model and by solving the radiation transport equation with the discrete transfer method. Simulations reproduced experimental data spanning a wide range of initial phenol concentrations, H2O2/phenol molar ratios and three values for lamp power. It was found that the velocity field depends on the volumetric flow rate: either it maintains a swirling motion through the whole reactor or might develop like a plug flow. The k-e model did not represent the RTD data accurately, and the velocity field therefore, since it is not appropriate for swirling flows. The other turbulence models showed good match of RTD, especially the k-w model. Simulations of phenol degradation deviated less than 8% from experimental data. It was possible verified that, due to the swirling inlet effects, reactants got concentrated close to the outer wall and migrated on the lamp direction along the reactor path. High radiation intensities close to the lamp surface created a layer around it where photolysis of H2O2 took place with higher rates. OH radicals were generated in that layer and transported towards the outer wall by convection. This caused most of phenol to be consumed in the second half of the reactor and accumulation of the radical near the lamp and the reactor outlet, since the pollutant in this area was already oxidized. The discrete transfer method predicted higher incident radiation intensity than the radial model, and higher concentrations of OH radicals as a consequence. Satisfactory results indicated that CFD was an appropriate tool for analyzing this reactive flow.

Os processos oxidativos avançados são promissores para a degradação de compostos orgânicos resistentes aos tratamentos convencionais, como o fenol. A fluidodinâmica computacional (CFD) tornou-se uma poderosa ferramenta para analisar processos fotoquímicos por resolver os balanços acoplados de quantidade de movimento, de massa e de radiação. O objetivo deste trabalho é investigar o processo UV/H2O2 num reator fotoquímico anular usando CFD e um modelo cinético mais realista. O modelo em CFD foi criado de forma progressiva. Inicialmente, foram determinados os campos de velocidade para três vazões (30, 60 e 100 L/h). Considerou-se dois diâmetros de lâmpada para reproduzir a configuração experimental do sistema. A discretização foi feita com malhas tetraédricas variando entre 390 000 e 1 200 000 elementos. Quatro modelos de turbulência RANS foram analisados: k-e, k-w, o shear stress transport (SST) e o modelo de tensões de Reynolds (RSM). O campo de velocidades foi validado comparando a DTR com seu levantamento experimental. A próxima etapa foi incluir o mecanismo de degradação de fenol proposto por Edalatmanesh, Dhib e Mehrvar (2008) no modelo em CFD. Trata-se de um modelo cinético baseado em equações dinâmicas para todas as espécies. O campo de radiação foi calculado pelo modelo radial e pela solução da equação de transporte de radiação através do método discrete transfer. As simulações reproduziram dados experimentais abrangendo uma larga gama de concentrações iniciais de fenol, razões molares H2O2/fenol e três potências de emissão das lâmpadas. O campo de velocidades obtido era dependente da vazão: o fluido pode manter movimento helicoidal sobre toda a extensão do reator ou se desenvolver como um escoamento pistonado. O modelo k-e não reproduziu bem o escoamento por não ser adequado para escoamentos rotativos. Os outros modelos geraram curvas de DTR com bom ajuste aos dados experimentais, especialmente o modelo k-w. O desvio médio entre as simulações de degradação de fenol e os dados experimentais é inferior a 8%. Verificou-se que, devido ao escoamento rotativo, os reagentes ficavam concentrados próximos à parede externa e migravam para a região da lâmpada ao longo do reator. A elevada intensidade de radiação na superfície da lâmpada criou uma camada ao seu redor na qual a fotólise do H2O2 ocorreu com grande taxa. Os radicais OH gerados nessa camada eram transportados para a região das paredes por convecção. Isso fez com que a maior parte do fenol fosse atacada na segunda metade do reator e gerou acúmulo do radical próximo à lâmpada na seção de saída do reator, já que o poluente já fora oxidado nessa área. O método discrete transfer previu intensidades de radiação maiores que o modelo radial, e, consequentemente, maior concentração de radicais OH. Os resultados satisfatórios indicam que CFD foi uma ferramenta adequada para analisar este escoamento reativo. / Advanced oxidation processes are a promising technology for degradation of organic compounds resistant to conventional treatments such as phenol. Computational fluid dynamics (CFD) has recently emerged as a powerful tool that allows a deeper understanding of photochemical processes in reactor engineering by solving the coupled momentum, mass and radiation balances. This work aimed to investigate the UV/H2O2 process in an annular photoreactor using CFD and a more realistic kinetic model. A progressive approach was used to develop the CFD reactor model. First, the velocity fields were determined for three volumetric flow rates (30, 60 and 100 L/h). Two lamp diameters were considered to reflect the experimental configuration of the system. Tetrahedral meshes varying form 390,000 to 1,200,000 elements were analyzed to achieve grid independence. For accounting turbulence effects, four RANS models were tested: k-e, k-w, the Shear Stress Transport (SST) and the Reynolds Stress models (RSM). The velocity field was validated through comparison to RTD experimental data. Next step was introducing the mechanism of phenol degradation proposed by Edalatmanesh, Dhib and Mehrvar (2008) into the CFD model. This kinetic model is based on dynamic equations for all species. The fluence rate field was calculated by the radial model and by solving the radiation transport equation with the discrete transfer method. Simulations reproduced experimental data spanning a wide range of initial phenol concentrations, H2O2/phenol molar ratios and three values for lamp power. It was found that the velocity field depends on the volumetric flow rate: either it maintains a swirling motion through the whole reactor or might develop like a plug flow. The k-e model did not represent the RTD data accurately, and the velocity field therefore, since it is not appropriate for swirling flows. The other turbulence models showed good match of RTD, especially the k-w model. Simulations of phenol degradation deviated less than 8% from experimental data. It was possible verified that, due to the swirling inlet effects, reactants got concentrated close to the outer wall and migrated on the lamp direction along the reactor path. High radiation intensities close to the lamp surface created a layer around it where photolysis of H2O2 took place with higher rates. OH radicals were generated in that layer and transported towards the outer wall by convection. This caused most of phenol to be consumed in the second half of the reactor and accumulation of the radical near the lamp and the reactor outlet, since the pollutant in this area was already oxidized. The discrete transfer method predicted higher incident radiation intensity than the radial model, and higher concentrations of OH radicals as a consequence. Satisfactory results indicated that CFD was an appropriate tool for analyzing this reactive flow.

[pt] O presente trabalho avalia a utilização de dois diferentes tipos de POA, Fenton-Zero - processo Fenton utilizando ferro zero valente: Fe0/H2O2 - e UV/H2O2 para o tratamento de efluente de indústria de celulose tratado biologicamente. Os parâmetros observados foram DBO, DQO, COT, cor e ABS280nm (medida de compostos ligninícos). Os experimentos foram conduzidos em batelada, em escala de laboratório e utilizando efluente real de indústria de celulose tratado biologicamente. Para os testes com o processo Fenton Zero foram realizados experimentos de acordo com um planejamento fatorial 2 elevado a 3, investigando a influência das variáveis pH, dosagem de peróxido de hidrogênio e massa de ferro zero valente fornecida por volume de solução. Como fonte de ferro foi utilizada lã de aço comercial nas concentrações de 5,5 g/L, 6,5 g/L e 7,5 g/L. As concentrações iniciais de peróxido de hidrogênio estudadas foram de 456,9 mg/L, 913,7 mg/L e 1370,6 mg/L e os valores de pH variaram entre 5.5, 6.5 e 7.5. Foram obtidas médias de remoção de 57,1 por cento de DQO, 67,2 por cento de DBO, 90,5 por cento de Cor, 83,4 por cento de compostos lignínicos e 54 por cento de COT, além de 9,52 mg/L de DBO final e 60,1 mg/L de DQO final. Já os testes com o sistema UV/H2O2 foram conduzidos com o único objetivo de polimento do efluente para reuso pelo processo. Desta maneira, o pH utilizado foi o natural do efluente (7,5) e três doses de H2O2 foram aplicadas, 4,0 g/L, 5,0 g/L e 6,0 g/L estando estas em excesso. / [en] The present work evaluates the use of two different types of AOP: the Zero-Fenton - process using zero valent iron - and UV/H2O2 for the treatment of pulp mill wastewater biologically treated. The observed parameters were BOD, COD, TOC, color and ABS280nm (measure of lignin compounds). The experiments were conducted in batch, lab scale and with real wastewater from biological treatment of a cellulose plant in Brazil. For the Fenton process, experiments were carried out according to a factorial design 23 investigating the influence of the variables pH, hydrogen peroxide dosage and zero-valent iron mass supplied by solution volume. As iron source, commercial steel wool was used in the concentrations of 5.5 g / L, 6.5 g / L and 7.5 g / L. The concentrations of hydrogen peroxide studied were 456.9 mg / L, 913.7 mg / L and 1370.6 mg / L and pH values ranged from 5.5, 6.5 and 7.5. The average removal rate was 57.1 per cent COD, 67.2 per cent COD, 90.5 per cent Color, 83.4 per cent lignin compounds and 54 per cent TOC. Also 9,52 mg/L of final BOD and 60,1 mg/L of final COD. The trials with the UV/H2O2 system, on the other hand, were conducted with the sole objective of polishing the effluent for reuse in the process. The pH used was the effluent s natural (7.5) and three excess doses of H2O2 were applied.

Persistent organic pollutants (POPs) are organic compounds of anthropogenic origin that have been linked to the development of cancer, neurobehavioural impairment, and immune system biochemical alterations. These chemicals have various industrial applications as well as acting as pesticides. Dioxins and furans are some of these compounds that are unintentionally produced in combustion and industrial processes. By definition these compounds have 4 common qualities: they are highly toxic, they are resistant to environmental degradation, they are introduced into the air and water where they travel long distances, and they accumulate in fatty tissues. Photochemical degradation is a method that has been extensively researched in the last few decades. In the aqueous phase it has already been shown to be able to degrade a number of refractory organics, such as dioxins and furans. The ultimate products of this process tend to be carbon dioxide, water, and mineral anions. Air phase work has been also gaining attention in recent decades as a possible alternative to incineration methods in air pollution control. The advantages of photochemical degradation processes are that they can be initiated at low temperatures, are relatively low cost compared to incineration processes, environmentally benign, and have the potential for quick and complete degradation of organic compounds. The main aim of the research is to investigate the photochemical degradation potential of PCDD/ PCDFs in gaseous air streams as a potential air pollution control technology. In order to do this, the photodegradation reaction kinetics were determined for chlorobenzene as a suitable surrogate for PCDD/PCDFs. Three different photodegradation schemes were employed: direct photolysis, UV/O3, and UV/H2O2. In addition, ozonolysis reaction rates were also determined to evaluate the effects of on the overall photodegradation rates for the UV/O3 process. Factors such as humidity levels and temperature were investigated to determine their effects on degradation rates. Temperature and humidity were not greatly influential on the degradation rates of direct photolysis. The degradation rate of chlorobenzene at a temperature of 100°C and high humidity was noticeably reduced, but unchanged at the 10% RH and 60% RH levels for all temperatures. Ozonolysis of chlorobenzene was negligible at 30°C for all humidity levels. Ozonolysis reactions at the 60°C and 100°C levels were higher than direct photolysis rates and in the 100°C case exceeded the UV/O3 degradation rates. Ozone coupled with UV experiments proved to be the most destructive at the low temperature of 30°C and molar ratio of 10:1 ozone to chlorobenzene. There was a clear and positive relationship between the amount of ozone present in the reactor and the degradation rate. At lower ozone to chlorobenzene molar ratios the degradation rates were not much higher than those for direct photolysis of ozone. The 5:1 molar ratio saw a significant increase in degradation rates over the photolysis rates. The fastest degradation rate was achieved for the 10:1 molar ratio and high humidity, which was over 10 times the rate of direct photolysis. In addition, humidity had a noticeably significant positive effect in these reactions. The effect of temperature on the UV/ozone reaction scheme was determined for the 5:1 ozone to chlorobenzene ratio. Temperature had an interesting effect on the degradation rates at higher temperatures. As the reactor temperature increased, the degradation rates from ozonolysis and UV/O3 began to converge at 60°C, ultimately leading to the ozonolysis reaction being faster than the UV/O3. Exploratory experiments for the H2O2 scheme were performed. H2O2 had a positive influence on the degradation rate of chlorobenzene and was about 26% higher than the direct photolysis rates. However for similar conditions, the UV/O3 process had higher degradation rates as was expected from the difference in absorption values between ozone and hydrogen peroxide.