CNPq / Florações de cianobactérias em reservatórios de abastecimento de água têm ocorrido com uma frequência cada vez maior, causando diversos problemas de ordem operacional nos sistemas de tratamento de água em decorrência da elevada densidade de células, além de preocupações quanto à eficiência do tratamento na remoção de metabólitos como cianotoxinas e compostos odoríferos. Este trabalho teve por objetivo avaliar a aplicabilidade da Moringa oleifera Lam pura e associada ao policloreto de alumínio (PACl) na remoção de células de Microcystis aeruginosa, microcistinas, 2-MIB e geosmina por meio de flotação por ar dissolvido e filtração rápida, utilizando carvão ativado granular. Primeiramente, os sais NaCl e CaCl2 foram avaliados para a extração do coagulante de M. oleifera. As amostras consistiram em água sintética adicionada de ácido húmico e células de M. aeruginosa para valores iniciais de 25 uT. O coagulante obtido com 1M CaCl2 de M. oleifera apresentou maior eficiência de remoção de cor, turbidez e número de células, sendo, para ele, indicada como ideal a dose de 50 mg L-1. É indicado que o CaCl2 não permite uma maior eficiência de extração do coagulante, mas sim que participe na formação dos flocos. A partir desses resultados, considerou-se a substituição de 10 a 50% do coagulante salino por PACl. O conjunto de coagulantes em proporções de 70:30 e 60:40 de M. oleifera e PACl permitiram uma melhoria na eficiência de remoção de células e redução do carbono orgânico residual. Finalmente, para essas proporções, foi avaliada a contribuição do uso de carvão ativado granular (CAG) como camada intermediária de filtro de areia visando à remoção de microcistinas, 2-MIB e geosmina. As amostras foram adicionadas de 50 ng L-1 de 2-MIB e geosmina, e 25 μg L-1 de microcistina-LR equivalente, antes dos ensaios. O uso do filtro com camada intermediária de CAG para o conjunto de coagulantes na proporção 70:30 (M.oleifera:PACl) resultou em eficiências globais acima de 95% para a remoção de cor, turbidez, células de M. aeruginosa, microcistinas e geosmina, e de 51 a 75% de remoção de 2-MIB e carbono orgânico dissolvido. Deste modo, o uso de M. oleifera como clarificante de águas com a substituição de 30% por PACl pode reduzir gastos com reagentes por parte de alguns países que hoje importam seu material para clarificação da água, e a adição de CAG no filtro de areia poderia reduzir custos e espaço com a instalação de mais de uma etapa para a remoção de metabólitos. Assim, este conjunto é indicado como uma alternativa de tratamento convencional de água, devido à sua capacidade de remoção de células e metabólitos, além da manutenção de cor, turbidez e microcistinas abaixo dos níveis estipulados para água de consumo. / Nutrient inputs leads to more frequent algal blooms in water supply reservoir which causes operational problems in water treatment plants due to high density of cells, aside from complications induced by its capacity of production of cyanotoxins and taste and odour compounds. The present study had as purpose an evaluation of the applicability of Moringa oleifera Lam as a coagulant with and without polyaluminium chloride (PACl) in the removal of Microcystis aeruginosa cells, microcystins, 2-MIB and geosmin using dissolved air flotation and filtration, using granulated activated carbon (GAC). First, NaCl and CaCl2 salts were studied for extraction of the coagulant. Samples were obtained by the addition of humic acid and M. aeruginosa cells in synthetic water in order to obtain 25 NTU. Coagulant obtained with 1M CaCl2 showed a better performance for color, turbidity and cells removal, being indicated 50 mg L-1 dosage. CaCl2 would not extract better the active component of M. oleifera seeds, but participate on flocs formation. Based on this, PACl addition was evaluated and added in the ranges of 10 to 50% substitution of the saline coagulant. 70:30 and 60:40 proportions of M.oleifera:PACl were indicated in order to to remove turbidity, color and cells. Finally, the use of GAC as an intermediate layer in rapid sand filtration bed was evaluated as a function of microcystins, 2-mib and geosmine retention capacity. Cited proportions were followed by filtration, added of 2-MIB and geosmin 50 ng L-1 as well as 25 μg L-1 of microcystin-LR equivalent before tests. A 70:30 (M.oleifera:PACl) proportion followed by rapid sand filtration combined with GAC led to removal efficiencies above 95% for color, turbidity, M. aeruginosa cells, geosmin and microcystins, and 51 to 75% efficiencies for 2-MIB and dissolved organic carbon. Hence, M. oleifera usage as water coagulant with 30% of PACl can reduce costs for some countries, and the addition of a GAC layer on a sand filter can reduce cost and space in water treatment plants. This process is indicated as an alternative conventional treatment for the removal of cyanobacteria cells and metabolites, besides its capacity to maintain turbidity, color and microcystins below the stipulated levels for water consumption.

CNPq / Florações de cianobactérias em reservatórios de abastecimento de água têm ocorrido com uma frequência cada vez maior, causando diversos problemas de ordem operacional nos sistemas de tratamento de água em decorrência da elevada densidade de células, além de preocupações quanto à eficiência do tratamento na remoção de metabólitos como cianotoxinas e compostos odoríferos. Este trabalho teve por objetivo avaliar a aplicabilidade da Moringa oleifera Lam pura e associada ao policloreto de alumínio (PACl) na remoção de células de Microcystis aeruginosa, microcistinas, 2-MIB e geosmina por meio de flotação por ar dissolvido e filtração rápida, utilizando carvão ativado granular. Primeiramente, os sais NaCl e CaCl2 foram avaliados para a extração do coagulante de M. oleifera. As amostras consistiram em água sintética adicionada de ácido húmico e células de M. aeruginosa para valores iniciais de 25 uT. O coagulante obtido com 1M CaCl2 de M. oleifera apresentou maior eficiência de remoção de cor, turbidez e número de células, sendo, para ele, indicada como ideal a dose de 50 mg L-1. É indicado que o CaCl2 não permite uma maior eficiência de extração do coagulante, mas sim que participe na formação dos flocos. A partir desses resultados, considerou-se a substituição de 10 a 50% do coagulante salino por PACl. O conjunto de coagulantes em proporções de 70:30 e 60:40 de M. oleifera e PACl permitiram uma melhoria na eficiência de remoção de células e redução do carbono orgânico residual. Finalmente, para essas proporções, foi avaliada a contribuição do uso de carvão ativado granular (CAG) como camada intermediária de filtro de areia visando à remoção de microcistinas, 2-MIB e geosmina. As amostras foram adicionadas de 50 ng L-1 de 2-MIB e geosmina, e 25 μg L-1 de microcistina-LR equivalente, antes dos ensaios. O uso do filtro com camada intermediária de CAG para o conjunto de coagulantes na proporção 70:30 (M.oleifera:PACl) resultou em eficiências globais acima de 95% para a remoção de cor, turbidez, células de M. aeruginosa, microcistinas e geosmina, e de 51 a 75% de remoção de 2-MIB e carbono orgânico dissolvido. Deste modo, o uso de M. oleifera como clarificante de águas com a substituição de 30% por PACl pode reduzir gastos com reagentes por parte de alguns países que hoje importam seu material para clarificação da água, e a adição de CAG no filtro de areia poderia reduzir custos e espaço com a instalação de mais de uma etapa para a remoção de metabólitos. Assim, este conjunto é indicado como uma alternativa de tratamento convencional de água, devido à sua capacidade de remoção de células e metabólitos, além da manutenção de cor, turbidez e microcistinas abaixo dos níveis estipulados para água de consumo. / Nutrient inputs leads to more frequent algal blooms in water supply reservoir which causes operational problems in water treatment plants due to high density of cells, aside from complications induced by its capacity of production of cyanotoxins and taste and odour compounds. The present study had as purpose an evaluation of the applicability of Moringa oleifera Lam as a coagulant with and without polyaluminium chloride (PACl) in the removal of Microcystis aeruginosa cells, microcystins, 2-MIB and geosmin using dissolved air flotation and filtration, using granulated activated carbon (GAC). First, NaCl and CaCl2 salts were studied for extraction of the coagulant. Samples were obtained by the addition of humic acid and M. aeruginosa cells in synthetic water in order to obtain 25 NTU. Coagulant obtained with 1M CaCl2 showed a better performance for color, turbidity and cells removal, being indicated 50 mg L-1 dosage. CaCl2 would not extract better the active component of M. oleifera seeds, but participate on flocs formation. Based on this, PACl addition was evaluated and added in the ranges of 10 to 50% substitution of the saline coagulant. 70:30 and 60:40 proportions of M.oleifera:PACl were indicated in order to to remove turbidity, color and cells. Finally, the use of GAC as an intermediate layer in rapid sand filtration bed was evaluated as a function of microcystins, 2-mib and geosmine retention capacity. Cited proportions were followed by filtration, added of 2-MIB and geosmin 50 ng L-1 as well as 25 μg L-1 of microcystin-LR equivalent before tests. A 70:30 (M.oleifera:PACl) proportion followed by rapid sand filtration combined with GAC led to removal efficiencies above 95% for color, turbidity, M. aeruginosa cells, geosmin and microcystins, and 51 to 75% efficiencies for 2-MIB and dissolved organic carbon. Hence, M. oleifera usage as water coagulant with 30% of PACl can reduce costs for some countries, and the addition of a GAC layer on a sand filter can reduce cost and space in water treatment plants. This process is indicated as an alternative conventional treatment for the removal of cyanobacteria cells and metabolites, besides its capacity to maintain turbidity, color and microcystins below the stipulated levels for water consumption.

Les procédés membranaires hybrides (PMH) allient la filtration membranaire basse pression à l’usage du charbon actif en poudre (CAP). Afin de diminuer les coûts opérationnels du procédé, il a été proposé de laisser vieillir le CAP dans le PMH et donc de minimiser le dosage de CAP frais. Peu d’information est disponible quant à la capacité résiduelle d’adsorption de suspensions de CAP âgées. L’importance relative de l’adsorption et de la biodégradation dans les réacteurs à CAP âgés sur le traitement des composés dissous est inconnue, ce qui empêche notamment l’optimisation du procédé. <p><p>Le principal objectif de ce projet de recherche est de décrire la performance du contacteur à CAP du PMH pour l’enlèvement de l’azote ammoniacal, du carbone organique dissous (COD), du COD biodégradable (CODB) et des micropolluants. Dans ce projet, l’emphase est placée sur l’opération du PMH avec de hauts temps de rétention de CAP. <p><p>La première phase de ce projet a consisté en une série de développements méthodologiques, base nécessaire à l’étude du CAP âgé. Des méthodes permettant la quantification de la biomasse hétérotrophe et nitrifiante colonisant le CAP âgé ont mis en évidence des densités de biomasse similaires à celle du charbon actif en grain en surface de filtre biologiques. L’irradiation aux rayons gamma a été démontrée comme une méthode adéquate pour produire des témoins abiotiques à partir de CAP de 10 et de 60 jours.<p><p>La seconde partie de cette étude s’est concentrée sur la démonstration de l’efficacité du PMH pour l’enlèvement de l’azote ammoniacal, du COD, ainsi que d’un mélange de micropolluants. Les cinétiques d’enlèvements ayant lieu au sein de des contacteurs à CAP ont été simulées en laboratoire sous diverses conditions (température, concentration en CAP, âge de CAP, matrice d’eau variable, temps de contact). Deux modèles cinétiques prédisant l’enlèvement de l’azote ammoniacal et du COD dans le PMH ont été développés sur base des simulations en laboratoire suivies sur CAP neuf, colonisé et abiotique. <p><p>De manière générale, les travaux réalisés au cours de ce doctorat ont mis en évidence le rôle majeur de l’adsorption résiduelle sur l’enlèvement de la contamination dissoute. Alors que l’enlèvement d’azote ammoniacal a majoritairement eu lieu par nitrification, le COD et les micropollutants sont principalement adsorbés sur le CAP colonisé. Il a aussi été montré que la capacité d’adsorption résiduelle des suspensions de CAP âgées peut agir en tampon, permettant de faire face à une augmentation soudaine de la concentration en azote ammoniacal, en COD ou en micropolluants. Le suivi des cinétiques d’enlèvement a permis de démontrer que la concentration, l’âge de CAP et le temps de rétention hydraulique (TRH) sont trois paramètres clefs pour l’optimisation du procédé. D’un point de vue économique, un TRH inférieur à 15 min est néanmoins désiré pour limiter les coûts du procédé. Par ailleurs, l’intérêt économique associé à l’augmentation de l’âge du CAP peut-être atténué par le besoin d’augmenter la concentration en CAP si l’adsorption est le mécanisme visé. De façon générale, ce projet démontre qu’une optimisation à l’échelle pilote du procédé est nécessaire car les objectifs de traitement, la qualité de l’eau à traiter et le fait que les 3 paramètres d’opération soient inter-reliés complexifient l’optimisation du PMH. Étant donné l’impact du TRH sur le coût du PMH, de futures recherches devraient viser à l’optimisation du mélange. <p>Hybrid membrane processes (HMPs) couple membrane filtration with powdered activated carbon (PAC). In HMPs, low-pressure membranes ensure an efficient particle removal, including protozoan parasites such as Cryptosporidium, while the PAC contactor is devoted to the removal of dissolved compounds. Such processes are emerging as a promising alternative to conventional treatment chains, which no longer allow the drinking water facilities to comply with increasingly stringent regulations on the treated water quality. To decrease the operating costs associated with virgin PAC consumption, it was suggested to let the PAC age in the PAC contactor of the process. Until now, the potential of using aged PAC in HMPs has been demonstrated for ammonia and DOC removal, but the potential to remove micropollutants remains unknown. It is suggested that the biological activity in aged PAC contactors contributes significantly to the removal of the dissolved compounds. Yet, neither the extent of the biomass on the aged PAC, nor the residual adsorption capacity, was quantified. No study focused on discriminating the mechanisms responsible for the treatment when using aged PAC suspensions. Most of the data published on HMPs using aged PAC were gathered at pilot scale under warm water conditions, yet the efficiency of the process is most likely sensitive to temperature changes. There is currently little information available on the efficiency of HMPs under cold water conditions. This lack of information hinders the optimization of the HMP, leading to sub-optimal usage of aged PAC.<p><p>The main objective of this research project is to describe the performance of the PAC contactor of HMPs in removing ammonia, dissolved organic carbon (DOC), biodegradable DOC (BDOC) and micropollutants. In particular, emphasis was placed on the operation of the HMP under high PAC residence times. On a more detailed level, the objectives of this project were (1) to develop and compare methods to quantify the biomass developed on aged PAC, (2) to develop a method to produce an abiotic control for aged PAC, (3) to characterize the removal kinetics of ammonia, DOC, BDOC and micropollutants occurring in the carbon contactor of an HMP, (4) to evaluate the impact of water temperature on the performance of the carbon contactor of an HMP, (5) to discriminate the relative importance of adsorption versus biological oxidation as mechanisms responsible for ammonia, DOC and micropollutants removal in the PAC contactor of an HMP, and finally (6) to differentiate the relative importance of the hydraulic retention time (HRT), the PAC age and the PAC concentration as key operating parameters on the optimization of the performance of the PAC contactor of an HMP.<p><p><p>To set the basis on the study of aged PACs, the first part of this research project consisted in methodological developments i) to quantify the heterotrophic and nitrifying biomass colonizing aged PAC, and ii) to create a reliable abiotic control of the colonized PAC, which is required for discriminating the mechanisms occurring on aged PAC. Heterotrophic and nitrifying biomass quantifying methods developed for colonized granular activated carbon (GAC) were successfully adapted to the aged PAC. The preferred methods were the potential 14C-glucose respiration (PGR) rate and the potential nitrifying activity (PNA), as they quantify the active heterotrophic and nitrifying biomass, which is most likely responsible for the depletion of BDOC and ammonia. An alternative method to the PGR, the potential acetate uptake (PAU) rate, was developed to alleviate the logistical and budgetary issues associated with the utilization of radio-labeled glucose. The densities (per gram of dry PAC) of both active heterotrophic and nitrifying biomasses were found comparable to that of the GAC sampled from the surface of a biological GAC filter. The gamma-irradiation was demonstrated as a reliable method to produce abiotic samples from soils, and was therefore chosen to produce abiotic colonized PAC samples in this project. In order to determine the optimized dosage of gamma-rays, increased doses were applied on PAC samples. Heterotrophic plate counts and methylene blue adsorption kinetics were used to determine respectively the lowest gamma ray dose required to inhibit the bacterial activity, and the highest dose that could be applied without affecting the aged PAC adsorption capacity and kinetics. Refractory DOC (RDOC) adsorption kinetics confirmed the accuracy of the dose chosen as the adsorptive behavior of the aged PAC was not affected. PGR rates were decreased 83% at the optimized dose. The gamma-irradiation method was therefore proven efficient and used in the following work phases of this research.<p><p>The second part of this study focused on the removal of ammonia, DOC and a mixture of micropollutants. Firstly, the PAC contactor of an HMP was simulated at lab-scale to monitor ammonia removal kinetics. Three PAC concentrations (approximately 1-5-10 g/L) of three PAC ages (0-10-60 days) were tested at two temperatures (7-22°C), in settled water with ambient influent condition (100 µg N–NH4/L) as well as under a simulated peak pollution scenario (1000 µg N–NH4/L). The kinetics evidenced that ammonia flux at pilot scale limited biomass growth (HRT = 67 min). In contrast, PAC colonization was not limited by the available surface and thus, PAC concentration was not a key operating parameter under the colonizing conditions tested (5-10 g/L). Ammonia adsorption was significant onto virgin PAC but the ammonia nitrification was crucial to reach complete ammonia removal at 22°C. When using colonized PAC, the 60-d PAC offered a better resilience to temperature decreases (78% at 7°C) as well as lower operating costs than the 10-d PAC (<10% at 7°C). Significant ammonia adsorption was also evidenced on 60-d PAC suspension, most probably due to PAC and the presence of suspended solids, but not on 10-d PAC. Adsorption and nitrifying activity were superior on 60-d PAC than on 10-d PAC at 7°C. In case of peak pollution, the process was most probably phosphate-limited but a mixed adsorption/nitrification still allowed 50% ammonia removal on 10-d and 60-d PAC at 22°C. A kinetics based model was developed to predict ammonia removals and to determine the relative importance of the adsorption and nitrification on colonized PAC under the conditions tested. <p><p>DOC, BDOC and RDOC removals occurring in the PAC contactor of an HMP were also simulated at lab-scale. Similar conditions to that of the ammonia removal kinetics were tested. The initial ammonia concentration remained untouched in the water matrices (settled water and raw water) but the BDOC-to-DOC ratio was altered by pre-ozonation (0 to 1.5 g O3/g C). The 10-d and 60-d abiotic controls were used to discriminate DOC adsorption from biodegradation. DOC biodegradation contributed marginally to DOC removal in the investigated conditions and DOC adsorption was increased at higher temperature. An original model integrating the PAC age distribution was developed to predict DOC removal in aged PAC contactors operated at steady-state. At a mean PAC residence time of 60-d, the younger PAC fraction (25-d and less) was primarily responsible for DOC adsorption (> 80%). This fraction represents 34% of the mass of PAC in the contactor. When using a water matrix with a higher initial DOC concentration (raw water) or a lower affinity for PAC (pre-ozonated settled water), the residual adsorption capacity of that older fraction was proven useful. <p><p>Lastly, a mixture of micropollutants (atrazine, deethylatrazine (DEA), linuron, microcystin, caffeine, carbamazepine, sulfamethoxazole, diclofenac, progesterone and medroxyprogesterone) was spiked at environmentally relevant concentrations (from 130 ng/L to 33 µg/L) in settled water (0 and 0.85 gO3/gC). The micropollutants concentration depletion was monitored over a period of 7h to 48 h on 1 g/L of 0-d, 10-d, 60-d PAC and gamma-irradiated 60-d PAC. Even in presence of NOM, the spiked micropollutants were rapidly adsorbed on aged PAC. No biodegradation was observed. Removals superior to 95% were reached within 5 minutes, and direct competition with NOM did not impact the efficiency of the process when micropollutants were spiked at environmentally relevant concentrations. Therefore, HMPs operated to remove DOC and ammonia can control transient micropollutant pollution and comply with the World health Organization recommendations for atrazine (2 µg/L) and microcystin (1 µg/L). However, the stricter European regulations for atrazine and DEA (0.1 µg/L) could not be met with 10-d and 60-d PAC under the operating conditions tested. Reaching such strict treatment objective would require a specific optimization of the process. <p><p>In general, this PhD research evidenced the role of the residual adsorption of aged PAC suspensions for the treatment of dissolved compounds. From the results obtained in this project, the potential of HMPs using aged PAC to remove micropollutants was evidenced. Additional research is however required to validate this potential under varied operating conditions. The modeling work improved the understanding of aged PACs. Finally, this research work provides original information on the optimization of HMPs. The optimization of the operating parameters will vary with the water quality targeted and the quality of the influent water. The PAC concentration, PAC age and HRT are inter-related. Therefore, it is recommended to optimize the operation of HMPs at pilot scale. Seasonal variations should be accounted for. An HRT of at least 15 min is required when the biological activity is mandatory to reach the water quality objectives. Lower HRT might be applied if adsorption is favored. Finally, as the HRT has a strong impact on the total cost of the process (capital and operational expenditure), PAC contactors’ hydraulic should be the point of focus of future research.& / Doctorat en Sciences agronomiques et ingénierie biologique / info:eu-repo/semantics/nonPublished

A presença de fármacos em águas superficiais, subterrâneas, solo e efluentes tem gerado preocupações no que diz respeito à ineficiência dos tratamentos convencionais e os riscos ambientais associados ao descarte inadequado destes micropoluentes emergentes. Diante disto, o objetivo deste trabalho foi avaliar a adsorção e a dessorção de ácido acetilsalicílico (AAS) em solução aquosa em carvão ativado de babaçu in natura (CAB) e funcionalizado quimicamente com HNO3 (CAA). Foram determinados aos adsorventes os teores de cinzas, umidade e de material volátil, granulometria, análise elementar, aspectos morfológicos dos adsorventes, por meio de microscopia eletrônica de varredura (MEV), pH no ponto de carga zero (pHPCZ), características da superfície dos adsorventes por meio de adsorção/dessorção de N2 e os grupos funcionais por espectroscopia na região no infravermelho (FTIR) e método de Boehm. Ensaios cinéticos, de equilíbrio e termodinâmicos foram conduzidos para a adsorção e dessorção em batelada. Ensaios em coluna de leito fixo foram conduzidos preliminarmente. Os resultados dos ensaios cinéticos de adsorção e dessorção foram ajustados aos modelos de pseudo-primeira e pseudo-segunda ordem e os resultados de equilíbrio de adsorção aos modelos matemáticos de Langmuir e Freundlich e de dessorção ao modelo de Langmuir-Freundlich. Aos resultados termodinâmicos de adsorção e dessorção foram determinados os valores de ΔG º, ΔH º e ΔS º. Os adsorventes apresentaram características microporosas, com valores de pHPCZ de 6,4 para CAB e 4,5 para CAA que interferem diretamente na adsorção. Os dados da cinética de adsorção foram melhor ajustados ao modelo de pseudo-segunda ordem e os do equilíbrio de adsorção ao modelo de Langmuir. Os resultados do ΔG º e ΔH º resultaram negativos e o do ΔSº positivo nas temperaturas de 25 ºC, 45 ºC e 55 ºC, indicando que o processo é exotérmico e espontâneo. O aumento da temperatura favoreceu a adsorção com o CAB, e reduziu a capacidade adsortiva do CAA. Em pH ácido a quantidade máxima adsorvida do AAS foi de 119,80 mg g -1 para CAB e 115,08 mg g -1 para CAA. Nos ensaios de dessorção os melhores resultados foram observados com o CAB em pHPCZ = 6,4. Os resultados cinéticos tiveram melhor ajuste ao modelo de pseudo-primeira ordem. As isotermas de dessorção ajustadas ao modelo de Langmuir-Freundlich. Adicionalmente, com os ciclos foram obtidos os percentuais médios de adsorção e dessorção de 92% e 75% no CAB e de 72% e 10% no CAA, respectivamente. O conjunto de dados de pH e temperatura avaliados nos ensaios em coluna de leito fixo determinaram que a reação de adsorção é melhor definida em pH 2,0 e temperatura de 40 ºC. / The presence of drugs in surface water, groundwater, soil and effluents has raised concerns regarding the inefficiency of conventional treatments and the environmental risks associated with the inappropriate disposal of these emerging micropollutants. The objective of this work was to evaluate the adsorption and desorption of acetylsalicylic acid (AAS) in aqueous solution of in natura activated babassu carbon (CAB) and chemically functionalized with HNO3 (CAA). The ash adsorbents, moisture and volatile matter, granulometry, elemental analysis, morphological aspects of the adsorbents were determined by scanning electron microscopy (SEM), pH at the zero load point (pHPCZ), surface characteristics of the adsorbents. adsorbents by adsorption/desorption of N2 and functional groups by infrared spectroscopy (FTIR) and Boehm method. Kinetic, equilibrium and thermodynamic tests were conducted for batch adsorption and desorption. Preliminary tests were conducted in a fixed bed column. The adsorption and desorption kinetics results were adjusted to the pseudofirst and pseudo-second order models and the adsorption equilibrium results to the Langmuir and Freundlich mathematical models. The values of ΔG º, ΔH º and ΔS º were determined for the thermodynamic adsorption and desorption results. The desorption equilibrium results were fitted to the Langmuir-Freundlich model. The adsorbents presented microporous characteristics, with values of pHPCZ of 6.4 for CAB and 4,5 for CAA that interfere directly in the adsorption. Adsorption was favored at acidic pH in both adsorbents. The adsorption kinetics data were better fitted to the pseudo second order model and those of the adsorption equilibrium to the Langmuir model, indicating the influence of the chemisorption on the adsorption. The results of ΔGº and ΔHº were negative and that of ΔSº positive at temperatures of 25 ºC, 45 ºC and 55 ºC, indicating the influence of the chemisorption in the process that is exothermic and spontaneous. The increase in temperature favored the adsorption with the CAB, and reduced the adsorptive capacity of the CAA. At acid pH the maximum adsorbed amount of ASA was 119.80 mg g -1 for CAB and 115.08 mg g -1 for CAA. In the desorption experiments the best results were observed with the CAB at pHPCZ = 6.4. The kinetic results had better fit to the pseudo first order model. Desorption isotherms fitted to the Langmuir-Freundlich model indicated affinity between the CAB, ASA and the chosen regenerant. Additionally, the average adsorption and desorption percentages of 92% and 75% in CAB and 72% and 10% in CAA, respectively, were obtained with the cycles. The set of pH and temperature data evaluated in the fixed bed column assays determined that the adsorption reaction is best defined at pH 2.0 and temperature of 40 ºC.

CAPES / Atualmente há preocupação da sociedade em relação aos impactos gerados pelas indústrias ao meio ambiente. Para produção de celulose e de papel é usada grande quantidade de água, madeira e produtos químicos, sendo gerado efluente nos diferentes processos produtivos da indústria. A matéria orgânica e a cor do efluente do processo Kraft se devem à presença de moléculas derivadas da lignina que são difíceis de serem removidas ou biodegradadas. Com vistas à remedição deste efluente, o presente trabalho busca avaliar a remoção de cor e matéria orgânica residual de efluente de celulose Kraft pré-tratado biologicamente, usando carvão ativado de casca de coco e argila montmorilonita pelo método de adsorção através de delineamentos experimentais. Para remoção de cor e matéria orgânica foram avaliados os fatores: a) pH do efluente; b) massa do material adsorvente no processo de adsorção e c) temperatura. A capacidade de adsorção de matéria orgânica e cor no carvão ativado e argila montmorilonita foram determinados pelo modelo matemático de Langmuir e Freundlich, por meio de ensaios de construção de isotermas de adsorção em efluente Kraft. O efluente foi caracterizado quanto a DQO, DBO5,20, COT e cor verdadeira antes e depois do tratamento terciário. Para o tratamento do efluente foram empregadas duas temperaturas: 25 e 40°C, seguiu-se planejamento fatorial completo 32 em triplicata com ponto central tendo como variáveis pH (5,0; 6,0 e 7,0) e massa de material adsorvente (0,5; 1,0 e 1,5 g). O planejamento experimental utilizado permitiu obter os melhores resultados com carvão ativado em 40 °C, pH 7,0 e 1,5 g de adsorvente com remoção de: 98% de COT, 83% de DQO, 97% de DBO5,20 e 95% de cor verdadeira e para argila em temperatura de 40 oC, pH 7, e 1,5 g de adsorvente com remoção de: 55% de COT, 50% de DQO, 90% de DBO5,20, e 56% de cor verdadeira. A principal variável responsável pela remoção de cor e matéria orgânica foi a massa de adsorvente seguida do pH. Também foi avaliada a possibilidade de aproveitamento do resíduo obtido a partir do processo de adsorção na incorporação de cinzas de carvão na produção de argamassas com teores de 0,4%, 1,0% e 1,2%; em cimento portland, areia e água com tempos de cura de 7 e 28 dias fazendo testes de resistência à compressão. Para a reutilização da argila foram utilizados 15% de argila do processo de adsorção, 25% de vidro e 60% de argila vermelha, para a confecção de corpos de prova cerâmico à temperatura de 1100 oC a 1150 oC. De modo geral, o processo de tratamento proposto neste trabalho utilizando carvão ativado, demostrou ser boa alternativa comparado com argila montmorilonita para redução de cor e matéria orgânica residual do efluente de processo Kraft, tendo-se em vista a utilização da cinza do carvão utilizado no processo de adsorção como um agregado para formação de argamassas na construção civil e argila utilizada na adsorção como material cerâmico. / Nowadays, there is a concern of society regarding the impacts caused by the industries on the environment. Large amounts of water, wood and chemichal are used to produce cellulose and paper, and contaminated effluents are generated through the various industrial processes associated. The organic matter and the color of the Kraft effluent are due to the presence of lignin-derived molecules that are difficult to be removed or biodegraded. With intent to remediate this effluent, this study aim to evaluate the removal of color and residual organic matter from biologically pretreated Kraft effluent, using activated carbon from coconut shell and montmorillonite clay by adsorption method through experimental designs. For the color and organic matter removal, the following factors were evaluated: a) pH of the effluent; b) the mass of the adsorbent material in the adsorption process and c) temperature. The adsorption capacity of organic matter and color in the activated carbon and in the montmorillonite clay were determined by the mathematical model of Langmuir and Freundlich, by means of isotherm adsorption construction in Kraft effluent.The effluent was characterized by COD, DBO5,20, COT and true color before and after the tertiary treatment. For it treatment two temperatures were employed: 25 °C and 40 °C, followed by a 32 full factorial design with center point in triplicate, using pH (5.0, 6.0 and 7.0) and masses of adsorbent material (0.5, 1.0 and 1.5 g) as variables. The experimental design used showed that the best results with activated carbon are obtained at 40 ° C, pH 7.0 and 1.5 g of adsorbent with removals of 98% of TOC, 83% of COD, 97% of BOD5,25 and 95% of true color. With clay, the best results occurred at temperature of 40 ° C, pH 7, and 1.5 g of adsorbent to remove 55% of COT, 50% of COD, 90% of BOD5,20 and 56% of true color. The main responsible for the removal of color and organic matter was the mass of adsorbent, followed by the pH. It was also evaluated the possibility of using the residue obtained from the adsorption process in the incorporation of carbon ash to produce mortars with levels of 0.4%, 1.0% and 1.2% in Portland cement, sand and water, with curing times of 7 and 28 days, for which compressive strength tests were performed. To reuse the clay, 15% of the clay from the adsorption process was used, together with 25% of glass and 60% of red clay, in order to construct ceramics bodies specimen generated at temperatures from 1100 °C to 1150 °C. The treatment process proposed in this work using activated carbon demonstrated to be, in general, a good alternative compared to montmorillonite clay for the color reduction and residual organic matter removal from Kraft process effluent, while residues from both process can be used as aggregates for mortars and ceramic body production.

CAPES; / As características do material suportem afetam diretamente a eficiência de um reator, pois o número e os tipos de células que aderem em cada meio suporte podem variar de um material para outro. A partir do desenvolvimento dos primeiros filtros anaeróbios um ponto crucial identificado pela comunidade científica foi a busca por materiais suportes que melhor se adequassem, ou seja, inertes à biomassa imobilizada, proporcionando bons resultados, facilidade operacional e economicamente viáveis. Uma alternativa é a utilização de materiais alternativos para preenchimento dos filtros, com estrutura resistente, biológica e quimicamente inerte, leveza, maior área específica e porosidade elevada, com possibilidade de colonização acelerada dos microrganismos e custos reduzidos. Neste trabalho foram avaliadas a estabilidade e o comportamento hidrodinâmico de três filtros anaeróbios de fluxo ascendente, operados de modo contínuo, preenchidos com diferentes meios suportes para imobilização da biomassa, sendo carvão vegetal, cerâmica de argila e borracha de pneu, no tratamento de água residuária sintética à base de glicose como fonte de carbono. Os filtros, em escala de bancada (1,3 L), foram operados com TDH de 8 h e 4 h em duas etapas e mantidos a temperatura ambiente. A caracterização físico-química dos materiais foi realizada com determinação dos parâmetros pH, massa específica aparente, densidade, teor de umidade, material volátil, teor de cinzas, número de iodo, porosidade, granulometria, análise da morfologia, área superficial, volume e tamanho dos poros. O comportamento dos filtros foi avaliado por meio da determinação dos parâmetros de pH, temperatura do líquido, alcalinidade total e a bicarbonato, ácidos voláteis e DQO nas amostras do afluente e do efluente. Além disso, foram realizados ensaios de estímulo-resposta tipo pulso com eosina Y como traçador para avaliar o comportamento hidrodinâmico do reator. O desempenho dos filtros em termos de pH, alcalinidade total e a bicarbonato e ácidos voláteis foi estável nas duas etapas de operação. Os valores obtidos em termos de DQO nas amostras do afluente e efluente dos filtros com carvão ativado foram: - Etapa I: 457 e 38 mg.L-1 (94% de remoção); - Etapa II: 291 e 79 mg.L-1 (79% de remoção); com cerâmica de argila foram: - Etapa I: 457 e 81 mg.L-1 (81% de remoção); - Etapa II:: 291 0 e 129 mg.L-1 (60% de remoção); e com borracha de pneu foram: - Etapa I: 457 e 58 mg.L-1 (88% de remoção); - Etapa II: 291 e 117 mg.L-1 (63% de remoção). O teste estatístico de Kruskal-Wallis. e o pósteste de Dunn confirmaram os dados experimentais e provaram que para maior parte dos parâmetros há diferença nos valores entre os filtros e entre as duas etapas. Sendo as diferenças obtidas entre os filtro devido as características distintas de cada material, e as diferenças entre as etapas ocorrem pelo aumento da carga hidráulica, pois o aumento da velocidade ascensional diminui o tempo de retenção celular e assim o grau de estabilidade. Contudo, meio suporte permitem aos filtros mais estabilidade e boas eficiências de degradação. / The characteristics of material directly affect the reactor efficiency, because the number and the types of cells what adhere in each material support can be totally different from material to another. From the development of the first anaerobic filters an important point identified by the scientific community was the search for materials that support better fitted, i.e. biomass immobilized inert, providing good results, operating ease and economically viable. An alternative is to use alternative materials for filling of filters, with sturdy structure, biologically and chemically inert, lightness, bigger specific area and high porosity, with possibility of rapid colonization of microorganisms and reduced costs. In this thesis it was evaluated the stability and the hydrodynamic behavior of three upflow anaerobic filter, operated in continuous mode, filled with different material support from immobilization to biomass being active carbon, clay ceramic and tire rubber in the synthetic wastewater treatment on based glucose as carbon source. The filter, in bench scale (1,3 L), was operated HRT to 8 hours and 4 hours in two steps Kept at ambient temperature. The physicochemical characterization of the materials was carried out with determination of parameters pH, bulk density apparent, density, moisture content, volatile material, ash content, iodine number, porosity, particle size, morphology analysis, surface area, volume and size pores. The behavior of the filters was evaluated by determining the parameters pH, liquid temperature, total and bicarbonate alkalinity, volatile acids and COD in samples of influent and effluent. Further, tests were performed stimulus-response type pulse with eosin Y, to evaluate the hydrodynamic regime of the reactor.The values obtained in terms of COD in samples of influent and effluent filters with activated carbon were: - Stage I: 457 and 38 mg.L-1 (94% of removal); - Stage II: 291 and 79 mg.L-1 (79% of removal), with clay ceramic were: - Stage I: 457 e 81 mg.L-1 (81% of removal); - Stage II: 291 and 129 mg.L-1 (60% of removal) and tire rubber were: - Stage I: 457 and 58 mg.L-1 (88% of removal); - Stage II: 291 and 117 mg.L-1 (63% of removal). The Kruskal-Wallis Statistical test and the Dun post-test confirmed the experimental data and proved from most part of parameters there is difference on values between the filters and between the two steps. Being the differences obtained between the filters due to distinct characteristics of each material, and the differences between the steps happened by hydraulic charging increased, because the ascending speed increased reduce the retention cellular therefore the degree of stability. However, material support allow the filters more stability and good degradation efficiencies.

CAPES / Atualmente há preocupação da sociedade em relação aos impactos gerados pelas indústrias ao meio ambiente. Para produção de celulose e de papel é usada grande quantidade de água, madeira e produtos químicos, sendo gerado efluente nos diferentes processos produtivos da indústria. A matéria orgânica e a cor do efluente do processo Kraft se devem à presença de moléculas derivadas da lignina que são difíceis de serem removidas ou biodegradadas. Com vistas à remedição deste efluente, o presente trabalho busca avaliar a remoção de cor e matéria orgânica residual de efluente de celulose Kraft pré-tratado biologicamente, usando carvão ativado de casca de coco e argila montmorilonita pelo método de adsorção através de delineamentos experimentais. Para remoção de cor e matéria orgânica foram avaliados os fatores: a) pH do efluente; b) massa do material adsorvente no processo de adsorção e c) temperatura. A capacidade de adsorção de matéria orgânica e cor no carvão ativado e argila montmorilonita foram determinados pelo modelo matemático de Langmuir e Freundlich, por meio de ensaios de construção de isotermas de adsorção em efluente Kraft. O efluente foi caracterizado quanto a DQO, DBO5,20, COT e cor verdadeira antes e depois do tratamento terciário. Para o tratamento do efluente foram empregadas duas temperaturas: 25 e 40°C, seguiu-se planejamento fatorial completo 32 em triplicata com ponto central tendo como variáveis pH (5,0; 6,0 e 7,0) e massa de material adsorvente (0,5; 1,0 e 1,5 g). O planejamento experimental utilizado permitiu obter os melhores resultados com carvão ativado em 40 °C, pH 7,0 e 1,5 g de adsorvente com remoção de: 98% de COT, 83% de DQO, 97% de DBO5,20 e 95% de cor verdadeira e para argila em temperatura de 40 oC, pH 7, e 1,5 g de adsorvente com remoção de: 55% de COT, 50% de DQO, 90% de DBO5,20, e 56% de cor verdadeira. A principal variável responsável pela remoção de cor e matéria orgânica foi a massa de adsorvente seguida do pH. Também foi avaliada a possibilidade de aproveitamento do resíduo obtido a partir do processo de adsorção na incorporação de cinzas de carvão na produção de argamassas com teores de 0,4%, 1,0% e 1,2%; em cimento portland, areia e água com tempos de cura de 7 e 28 dias fazendo testes de resistência à compressão. Para a reutilização da argila foram utilizados 15% de argila do processo de adsorção, 25% de vidro e 60% de argila vermelha, para a confecção de corpos de prova cerâmico à temperatura de 1100 oC a 1150 oC. De modo geral, o processo de tratamento proposto neste trabalho utilizando carvão ativado, demostrou ser boa alternativa comparado com argila montmorilonita para redução de cor e matéria orgânica residual do efluente de processo Kraft, tendo-se em vista a utilização da cinza do carvão utilizado no processo de adsorção como um agregado para formação de argamassas na construção civil e argila utilizada na adsorção como material cerâmico. / Nowadays, there is a concern of society regarding the impacts caused by the industries on the environment. Large amounts of water, wood and chemichal are used to produce cellulose and paper, and contaminated effluents are generated through the various industrial processes associated. The organic matter and the color of the Kraft effluent are due to the presence of lignin-derived molecules that are difficult to be removed or biodegraded. With intent to remediate this effluent, this study aim to evaluate the removal of color and residual organic matter from biologically pretreated Kraft effluent, using activated carbon from coconut shell and montmorillonite clay by adsorption method through experimental designs. For the color and organic matter removal, the following factors were evaluated: a) pH of the effluent; b) the mass of the adsorbent material in the adsorption process and c) temperature. The adsorption capacity of organic matter and color in the activated carbon and in the montmorillonite clay were determined by the mathematical model of Langmuir and Freundlich, by means of isotherm adsorption construction in Kraft effluent.The effluent was characterized by COD, DBO5,20, COT and true color before and after the tertiary treatment. For it treatment two temperatures were employed: 25 °C and 40 °C, followed by a 32 full factorial design with center point in triplicate, using pH (5.0, 6.0 and 7.0) and masses of adsorbent material (0.5, 1.0 and 1.5 g) as variables. The experimental design used showed that the best results with activated carbon are obtained at 40 ° C, pH 7.0 and 1.5 g of adsorbent with removals of 98% of TOC, 83% of COD, 97% of BOD5,25 and 95% of true color. With clay, the best results occurred at temperature of 40 ° C, pH 7, and 1.5 g of adsorbent to remove 55% of COT, 50% of COD, 90% of BOD5,20 and 56% of true color. The main responsible for the removal of color and organic matter was the mass of adsorbent, followed by the pH. It was also evaluated the possibility of using the residue obtained from the adsorption process in the incorporation of carbon ash to produce mortars with levels of 0.4%, 1.0% and 1.2% in Portland cement, sand and water, with curing times of 7 and 28 days, for which compressive strength tests were performed. To reuse the clay, 15% of the clay from the adsorption process was used, together with 25% of glass and 60% of red clay, in order to construct ceramics bodies specimen generated at temperatures from 1100 °C to 1150 °C. The treatment process proposed in this work using activated carbon demonstrated to be, in general, a good alternative compared to montmorillonite clay for the color reduction and residual organic matter removal from Kraft process effluent, while residues from both process can be used as aggregates for mortars and ceramic body production.

CAPES; / As características do material suportem afetam diretamente a eficiência de um reator, pois o número e os tipos de células que aderem em cada meio suporte podem variar de um material para outro. A partir do desenvolvimento dos primeiros filtros anaeróbios um ponto crucial identificado pela comunidade científica foi a busca por materiais suportes que melhor se adequassem, ou seja, inertes à biomassa imobilizada, proporcionando bons resultados, facilidade operacional e economicamente viáveis. Uma alternativa é a utilização de materiais alternativos para preenchimento dos filtros, com estrutura resistente, biológica e quimicamente inerte, leveza, maior área específica e porosidade elevada, com possibilidade de colonização acelerada dos microrganismos e custos reduzidos. Neste trabalho foram avaliadas a estabilidade e o comportamento hidrodinâmico de três filtros anaeróbios de fluxo ascendente, operados de modo contínuo, preenchidos com diferentes meios suportes para imobilização da biomassa, sendo carvão vegetal, cerâmica de argila e borracha de pneu, no tratamento de água residuária sintética à base de glicose como fonte de carbono. Os filtros, em escala de bancada (1,3 L), foram operados com TDH de 8 h e 4 h em duas etapas e mantidos a temperatura ambiente. A caracterização físico-química dos materiais foi realizada com determinação dos parâmetros pH, massa específica aparente, densidade, teor de umidade, material volátil, teor de cinzas, número de iodo, porosidade, granulometria, análise da morfologia, área superficial, volume e tamanho dos poros. O comportamento dos filtros foi avaliado por meio da determinação dos parâmetros de pH, temperatura do líquido, alcalinidade total e a bicarbonato, ácidos voláteis e DQO nas amostras do afluente e do efluente. Além disso, foram realizados ensaios de estímulo-resposta tipo pulso com eosina Y como traçador para avaliar o comportamento hidrodinâmico do reator. O desempenho dos filtros em termos de pH, alcalinidade total e a bicarbonato e ácidos voláteis foi estável nas duas etapas de operação. Os valores obtidos em termos de DQO nas amostras do afluente e efluente dos filtros com carvão ativado foram: - Etapa I: 457 e 38 mg.L-1 (94% de remoção); - Etapa II: 291 e 79 mg.L-1 (79% de remoção); com cerâmica de argila foram: - Etapa I: 457 e 81 mg.L-1 (81% de remoção); - Etapa II:: 291 0 e 129 mg.L-1 (60% de remoção); e com borracha de pneu foram: - Etapa I: 457 e 58 mg.L-1 (88% de remoção); - Etapa II: 291 e 117 mg.L-1 (63% de remoção). O teste estatístico de Kruskal-Wallis. e o pósteste de Dunn confirmaram os dados experimentais e provaram que para maior parte dos parâmetros há diferença nos valores entre os filtros e entre as duas etapas. Sendo as diferenças obtidas entre os filtro devido as características distintas de cada material, e as diferenças entre as etapas ocorrem pelo aumento da carga hidráulica, pois o aumento da velocidade ascensional diminui o tempo de retenção celular e assim o grau de estabilidade. Contudo, meio suporte permitem aos filtros mais estabilidade e boas eficiências de degradação. / The characteristics of material directly affect the reactor efficiency, because the number and the types of cells what adhere in each material support can be totally different from material to another. From the development of the first anaerobic filters an important point identified by the scientific community was the search for materials that support better fitted, i.e. biomass immobilized inert, providing good results, operating ease and economically viable. An alternative is to use alternative materials for filling of filters, with sturdy structure, biologically and chemically inert, lightness, bigger specific area and high porosity, with possibility of rapid colonization of microorganisms and reduced costs. In this thesis it was evaluated the stability and the hydrodynamic behavior of three upflow anaerobic filter, operated in continuous mode, filled with different material support from immobilization to biomass being active carbon, clay ceramic and tire rubber in the synthetic wastewater treatment on based glucose as carbon source. The filter, in bench scale (1,3 L), was operated HRT to 8 hours and 4 hours in two steps Kept at ambient temperature. The physicochemical characterization of the materials was carried out with determination of parameters pH, bulk density apparent, density, moisture content, volatile material, ash content, iodine number, porosity, particle size, morphology analysis, surface area, volume and size pores. The behavior of the filters was evaluated by determining the parameters pH, liquid temperature, total and bicarbonate alkalinity, volatile acids and COD in samples of influent and effluent. Further, tests were performed stimulus-response type pulse with eosin Y, to evaluate the hydrodynamic regime of the reactor.The values obtained in terms of COD in samples of influent and effluent filters with activated carbon were: - Stage I: 457 and 38 mg.L-1 (94% of removal); - Stage II: 291 and 79 mg.L-1 (79% of removal), with clay ceramic were: - Stage I: 457 e 81 mg.L-1 (81% of removal); - Stage II: 291 and 129 mg.L-1 (60% of removal) and tire rubber were: - Stage I: 457 and 58 mg.L-1 (88% of removal); - Stage II: 291 and 117 mg.L-1 (63% of removal). The Kruskal-Wallis Statistical test and the Dun post-test confirmed the experimental data and proved from most part of parameters there is difference on values between the filters and between the two steps. Being the differences obtained between the filters due to distinct characteristics of each material, and the differences between the steps happened by hydraulic charging increased, because the ascending speed increased reduce the retention cellular therefore the degree of stability. However, material support allow the filters more stability and good degradation efficiencies.