Nitrogen is the major component of biosphere. Paradoxically, nitrogen pollution is the concern globally. Ammonia pollution is due to its unceasing rejection into nature such as groundwater, current water and the atmosphere. This phenomenon constitutes a threat for the humanity, land and aquatic flora, and consequently disturbs the balance of natural ecosystem. Recently, that situation has lead to develop various techniques and/or technologies for ammonia removal from municipal and industrial wastewaters. Particularly in the environmental biotechnology area, two main objectives were recently aimed in many research activities: the development of new configurations of competitive bioreactors and the monitoring of partial nitrification process, which are the fundamental basis of this thesis project. In this study, the partial ammonium oxidation process, also called nitrite route, was studied in a 60 litre jet-loop submerged membrane bioreactor pilot plant. The research was organized around six chapters. An exhaustive literature review of the state-of- art of the biological nitrification process and the membrane technologies was performed. The materials and measurement methods were presented. The colorimetric method, the chromatography analysis, the biomass estimation by the suspended solids (SS), the aggregates size measurement, the gas holdup, the gas-liquid mass transfer, the bubbles gas diameter determination, the medium rheology aspects, etc., and the complete equipment of the bioreactor were studied in detail. The plant automation functioning was also studied. Membrane module (Mitsubishi Sterapore-L) characterization was carried out and three characteristic parameters were estimated: the membrane intrinsic resistance Rm, the membrane permeability Lp and the membrane porosity εm. Estimations revealed good agreement between experimental results and theoretical methods based on the Darcys law and the Carman-Kozeny law applicable in microfiltration system. Hydrodynamics and aeration aspects were studied. The mixing in the jet-loop system was characterized by the mixing time (tmix) and the circulation time (tc), respectively. The results showed that the characteristic times (tmix and tc) decrease with an increase in input gas flowrate and the circulated liquid flowrate. A model correlation involving the air and the combined liquid effects was proposed to describe the circulation time evolution. The classical non-steady state clean water test was used to determine the gas-liquid mass transfer coefficient (kLa). It was found to be influenced by the combined action of air and recirculated-liquid flowrates and a correlation has been proposed to describe their influence. The interpretation of kLa results and the system mixing data showed that the developed reactor corresponds to a near perfect mixing tank. This criterion was satisfactorily verified by literature data. The gas holdup (εg) was directly measured by the volume expansion method. In the absence of liquid circulation, εg ranged between 1 and 4% for the investigated range of gas liquid superficial velocities. It was found to increase linearly with the air superficial velocity, which corresponds to the bubbly flow regime. However, in the presence of liquid flowrate, εg slightly increased (from 1 to 6%) with increase in the superficial liquid velocity. A model has been proposed to correlate εg and the air and the recirculated-liquid velocities. The average diameter of the bubbles gas (dB) in the system was also estimated by the Leibson theoretical model based on the Reynolds number at the orifice of the gas distributor. Finally, biological aspects were studied. Respirometry measurements were conducted to characterize the process medium. The mass transfer, the gas holdup and the medium viscosity were determined. The obtained data allowed estimating the α factor and the β factor, respectively. The interaction of the growth of microorganisms into the process and the membrane performance was also investigated and a correlation model was proposed to describe membrane fouling with time. The optimal conditions for ammonium partial oxidation were determined using process monitoring and simulation. Dissolved oxygen (DO), temperature (T) and hydraulic retention time (HRT) were selected to achieve a high nitrite accumulation in the system. The results obtained showed that the selected parameters should be fixed at DO ≈ 2 mgO2.l-1, HRT ≈ 6 7 h and T = 30°C, respectively. The partial nitrification was simulated by the use of the TwoPopNitrification model included into the BioWin 2.2 software. For these simulations, a sequencing ammonia oxidation assumption was adopted: the nitrozation followed by the nitration step, respectively. The corresponding kinetics and stoichiometric constants were estimated by combining literature data and experimental nitrification results. For these estimates, the ammonium oxidation was monitored on several process samples taken at different times. The estimates were also delivered by monitoring the ammonium oxidation on the process operated in the batch mode. The plotting of simulations and experimental results revealed good agreement. In order to investigate the process performance in terms of biological stability, a long time period (≈ 600 days) was simulated. The results showed that a high stable nitrite accumulation (> 95%) could be achieved when the above optimal conditions are imposed to the system. However, after a long time, the accumulated nitrite is converted into nitrate and then the system is disrupted. For the simulated experimental conditions, the process disruption period was located between 180 and 350 days. At this period, a corresponding theoretical purge flowrate was found to range between 0.15 10-3 m3.d-1 and 3.0 10-3 m3.d-1. Simulations also showed that increasing the purge flowrate decreases the sludge retention time and then favours nitrite accumulation into the process. That is an interesting strategy to increase the performance of the biological partial nitrification process.

Biological nitrogen removal was simulated for a Vacuum Rotating Membrane (VRM) type membrane bioreactor (MBR) operated in METU campus. In order to simulate the biological MBR plant, a dynamic model that describes the process is needed. In this thesis, the Activated Sludge Model No.1 (ASM1), which still is the most widely used model developed by the International Association on Water Quality (IAWQ), has been used to simulate the carbon oxidation, nitrification and denitrification processes occurring in the plant using AQUASIM software package. Once the model was established, sensitivities of the model parameters were analyzed. Then, parameter estimation was carried out for the optimization of the sensitive parameters. As we have several distinct data sets available two parallel modeling study was carried out for the calibration of the model. Finally, the calibrated model by different data sets was validated by using the remaining data sets. The model results were consistent with the measured data especially in terms of MLSS concentration in the system. However model results for the nitrogen removal were not extremely successful / the reason for this might be the inadequate available data on nitrification-denitrification process occurring in the system.

Centralized infrastructure (CI) is difficult to sustain with limited water and fossil fuel resources because CI withdraws 100% of water demand from the environment as an open-loop system and electricity is consumed to transport and treat water and wastewater while demand is increasing. Hybrid infrastructure (HI) is proposed to combine CI with decentralized alternatives such as low impact development (LID) technologies (i.e., xeriscaping, rain gardens, and rainwater harvesting) or greywater reclamation systems with membrane bioreactors (MBRs). Water, wastewater, and stormwater systems in the City of Atlanta (COA) were regarded as CI. HI was compared to CI using life cycle environmental impacts measured by water reuse index (WRI) and life cycle assessment (LCA) scores. WRI is a ratio of water withdrawal to sustainable water resources of wastewater (i.e., return flow) and stormwater discharge, which presents water stress level (e.g., 0.2 ~ 0.4: medium-high level). LCA score is determined as % of annual world average environmental damage per capita. As stormwater runoff, water demand, greywater generation, rainwater harvesting, etc. vary depending on land use and population density, feasibility of decentralized alternatives was evaluated in eleven residential communities. Five single-family residential communities were designated as between R-1 of 16 people/10 acres and R-5 of 169 people/10 acres and six multi-family residential communities were designated as between RG-1 of 148 people/10 acres and RG-6 of 5,808 people/10 acres. HI with LID technologies reduced WRI of COA that relies on CI from 0.45 to 0.12. HI reduced the LCA scores of CI with combined sewer system (CSS) by between 1% for RG-6 and 68% for R-1 and the LCA scores of CI with separate sewer system (SSS) by between 0% for RG-6 and 18% for R-1. As population density increases for the multi-family residential communities, harvested rainwater decreases and a small amount of water demand is satisfied. Consequently, it has a negligible impact on the LCA scores in RG-6. HI with greywater reclamation system reduced WRI of COA from 0.45 to 0.35. HI resulted in the LCA scores greater as compared to CI in the five single-family communities and RG-1, RG-2, and RG-3 because of the electricity consumption of small-scale MBR. However, the electricity consumption per kgal decreases with increasing MBR treatment capacity and the LCA scores were reduced by 5% for RG-4, 15% for RG-5, and 21% for RG-6. The MBR treatment capacity of RG-4 is 15.6 kgal/day.

Particles and macromolecular components, including biopolymers (protein and carbohydrate), are viewed as the main foulants in the complex feed submerged membrane filtration systems such as membrane bioreactor (MBR). This work focused on two aspects of fouling in complex fluids: 1- Assessing fouling propensity and mechanisms for various model solutions. 2- Using of two specific solutions modelling biomass found in MBR for a better understanding of the fouling mechanisms in submerged MBR processes. Filtrations were carried out with 0.22 ??m PVDF hollow fibre membrane. Alginate was used as a model for polysaccharide, bovine serum albumin (BSA) as a model for protein, (un)washed yeast and bentonite were representing suspended solid contents. According to the data obtained during this study the fouling propensity of each model solution was classified as follow in a decreasing order: Alginate &gt unwashed yeast &gt washed yeast &gt BSA &gt bentonite for one-component solutions; and Alginate-washed yeast &gt Alginate-BSA &gt Alginate-bentonite &gt Alginate-unwashed yeast for two-component solutions. Introducing the alginate increased the reversible fouling (except BSA). Passive adsorption had a significant effect on fouling of alginate even before the beginning of the filtration. Washed yeast and a mixture of washed yeast + BSA were then used as model solutions to simulate the activated sludge found in MBR. The concentration of washed yeast and BSA used in this study were calculated in order for the characterisations of the two model solution to match (in terms of biopolymer contents) those of MBR biomasses reported in the literature. By rinsing, backwashing and chemical cleaning of the membrane, three fouling layers of upper, intermediate and lower were defined respectively. Results obtained from the analysis of the biopolymers found in the cleaning solutions allow a better understanding of the fouling mechanisms occurring for the two model solutions used in this study: for washed yeast, the lower layer and for washed yeast + BSA , the upper and intermediate layers were found to have relatively high biopolymeric composition. This was explained by higher concentration of solids on the membrane surface and by higher biopolymer interactions when washed yeast was mixed with BSA.

Les procédés de réutilisation des eaux usées doivent être robustes, fiables et rentables pour que leur utilisation se démocratise et devienne complémentaire des traitements des eaux de surface. Le couplage d’un procédé biologique et de procédés membranaires représente une solution prometteuse pour répondre à ces challenges. Cette étude se focalise sur l’impact des conditions de fonctionnement du procédé secondaire (en particulier par bioréacteur à membrane BAM) sur le colmatage du procédé tertiaire de nanofiltration (NF) ou d’osmose inverse (OI) ainsi que sur le devenir des micropolluants et microorganismes tout au long de la chaine de traitement. Dans un premier temps, des expériences à court terme de filtration avec différentes membrane NF et d’OI ont été réalisées afin de caractériser les interactions entre effluents secondaires et membranes. Il a ainsi été observé de très fortes rétentions de tous les micropolluants ciblés par la Directive Cadre Européenne. En termes de colmatage, la chute de flux de l’OI, essentiellement liée pour ces essais de courte durée à une augmentation de pression osmotique puis à un dépôt de cristaux minéraux, peut être maîtrisée en contrôlant le pH et la concentration en carbonate et phosphate de l’effluent secondaire. Par ailleurs, des chutes de flux plus importantes sont observées lors des filtrations réalisées avec les membranes de NF qui sont plus sensibles au colmatage irréversible. Dans un second temps, l’optimisation de la filière de traitement des eaux usées urbaines couplant un bioréacteur à membranes à un procédé d’OI a été réalisée à partir d’une unité pilote fonctionnant en continu. La sélection de conditions opératoires adéquates a permis de faire fonctionner le procédé d’OI pendant plus de quatre mois sans qu’aucune maintenance ne soit réalisée. Une faible chute de flux de l’OI, linéaire sur toute la période de filtration, essentiellement dû à l’adsorption de molécules organiques à la surface de la membrane, a été observée. Sur l’ensemble de la période d’essais, la filière BAM/OI permet d’obtenir un abattement optimal en micropolluants présents. Lorsque des micropolluants sont injectés à des concentrations plus élevées (simulation d’une brusque dégradation de la qualité des eaux en entrée de filière) dans le bioréacteur, une chute de l’activité de la biomasse couplée à un relargage de produits microbiens solubles peut être observée. Néanmoins, ces pics de pollution n’ont eu aucun impact sur le colmatage de la membrane du BAM ni sur celle de l’OI. La filière BAM-OI permet donc de garantir un taux de rejet élevé et une productivité d’environ 15 L.h-1.m2 quelles que soient les fluctuations de la composition de l’eau usée urbaine à traiter. / In order to be competitive compare to surface water treatments, wastewater reuse needs robust, reliable and profitable combination of technologies. The combination of bioreactors and membrane processes seems to be a promising solution to these challenges. This study focus on the impact of the operating conditions of the secondary treatment (particularly the membrane bioreactor (MBR)) on the nanofiltration (NF) and reverse osmosis (RO) tertiary treatments as well as the fate of micropollutants and microorganisms along the treatment line. Firstly, short term filtration experiments with various NF and RO membranes were performed in order to characterize the interactions between secondary treatment effluents (STE) and membranes. High retentions of micropollutants listed by the European water framework directive were observed. During these short term experiments, RO flux decline is mainly due to an increase of osmotic pressure and then a precipitation of salts that can be solved by controlling the pH and thus the carbonate and phosphate concentration of the STE. In addition, higher flux declines are observed with NF because of a higher irreversible fouling behavior. Secondly, continuous long term tests were performed on a pilot unit combining a MBR and a RO processes. The appropriate selection of operating conditions allowed treating wastewater during more than four months without any maintenance. A linear low flux decline, mainly due to adsorption of organic molecules at the membrane surface was observed. During this filtration period, the MBR/RO process presented very high micropollutant retentions. When micropollutants are injected at higher concentration (simulation of sudden fluctuation of feed composition) into the MBR, a drop of biomass activity combined with soluble microbial products release can be observed. Nevertheless, these peaks of pollution did not cause any additional fouling of MBR as well as RO membranes. MBR/RO process is then a reliable technology that can guaranty high retention and productivity (around 15 L.h-1.m-2) whatever the fluctuations of the feed composition.

Le colmatage membranaire demeure l’un des verrous majeurs des bioréacteurs à membrane (BAM). Ces travaux visent à apporter une contribution à la compréhension de la dynamique de structuration de dépôts complexes formés lors de la filtration frontale de (bio)fluides et son impact sur les performances de filtration. Pour cela, différents outils permettant la mesure in-situ des propriétés structurelles locales des dépôts ont été utilisés de manière à pouvoir relier ces propriétés aux performances globales de filtration. Les propriétés électrocinétiques des dépôts ont également été étudiées. Deux méthodes, l’une optique et l’autre acoustique, ont été utilisées pour caractériser les propriétés structurelles locales des dépôts (épaisseur, cinétique de croissance). Dans un premier temps, les épaisseurs obtenues par les méthodes optiques et acoustiques ont été comparées. Il a été montré que, dans le cas de dépôts peu poreux, les deux méthodes conduisent aux mêmes épaisseurs de dépôts. Dans le cas de dépôts plus poreux, ces deux méthodes permettent l’obtention de données complémentaires à deux niveaux de profondeur différents au sein du dépôt. L’influence des conditions opératoires sur la structuration de dépôts de particules modèles a ensuite été étudiée. Grâce à la méthode optique il a été montré que, quelles que soient les conditions opératoires, il existe une variation temporelle des propriétés du dépôt. De plus, une répartition non homogène du dépôt à la surface de la membrane peut également exister, favorisée par de faibles répulsions entre particules. Enfin, l’applicabilité des différentes méthodes au cas des biofluides issus de BAM a été évaluée. La structure de dépôts complexes constitués lors de la filtration de ces biofluides a ensuite été étudiée. La compressibilité des dépôts, mise en évidence à l’échelle globale par suivi des performances de filtration, a également été observée à l’échelle locale : l’épaisseur du dépôt décroît avec une augmentation de la PTM. De plus, à l’échelle locale, une variabilité spatiale des propriétés du dépôt a été mise en évidence. Afin de contrôler la compressibilité des dépôts l’impact de l’ajout de particules au sein du biofluide a été évalué / Membrane fouling is one of the major drawbacks of membrane bioreactors. This study is thus a contribution to the understanding of the dynamic structuring of complex deposits build-up during dead-end filtration of complex biofluids. Several tools were used to perform in-situ characterization of cake layer structural properties at local scale and to link them to global filtration performances. The electrokinetics properties of the deposit were also investigated. An optical and an acoustic method were used to measure local cake thickness and growth kinetics. The thicknesses given by the two methods were first compared. It was shown that for compact deposits the two different methods lead to the same thickness of the deposit. For more porous deposits, these two methods allow to obtain complementary data at two different depths of the deposits. The influence of operating conditions on cake layer structuring during filtration of modelled particles was evaluated. Using the optical method it was shown that, whatever the operating conditions, the cake structure is not constant in time. Furthermore, a spatial variability of the cake layer thickness might exist especially in the case of weak particle-particle repulsion. Finally, it has been investigated whether the different methods could be applied or not to the case of biofluid filtration. The structural properties of the complex deposits built up during diluted activated sludge filtration were investigated. Cake compressibility was observed at global scale by a monitoring of process performances and was also observed at local scale: cake thickness decreases as TMP increases. Furthermore, at local scale, a spatial variability of deposit structure was found. Particle addition into the biofluid was assessed in order to mitigate compressibility effects

O processo de Biorreatores com Membranas (BRM) foi desenvolvido no final da década de 1960, consistindo em um sistema que associa o tratamento biológico de efluentes com o mecanismo de separação por membranas, e apresenta vantagens com relação ao tratamento convencional, tais como maior eficiência de tratamento e um menor espaço físico de instalação para a mesma capacidade de tratamento. O fenômeno de incrustação das membranas (em inglês, fouling) representa a principal limitação desse processo, de modo que uma das condições operacionais mais importantes na prevenção da incrustação em um sistema BRM Submerso (BRMS) é a vazão de aeração. Diante desta situação, o objetivo do trabalho consiste em avaliar os efeitos das condições hidrodinâmicas no desempenho do processo, tais como vazão de aeração, densidade de empacotamento do módulo de membranas e geometria dos aeradores. O sistema utilizado no trabalho consistiu em um BRMS automatizado, operando em pressão constante e de forma contínua, durante um período de 4 dias. Os módulos foram construídos com membranas poliméricas de microfiltração do tipo fibra oca, cujo material foi a poli(éter)-imida (PEI). Três diferentes vazões de aeração foram estudadas (2, 5 e 8 L.min-1), mostrando, a partir dos resultados, que existe uma vazão de aeração limite benéfica ao sistema e que, acima deste valor, um melhor desempenho não pode ser atingido, inclusive, podendo prejudicá-lo. Para o sistema de estudo, a vazão de 5 L.min-1 apresentou o melhor desempenho, seguido de 8 e 2 L.min-1. O estudo da densidade de empacotamento do módulo mostrou que esta é uma variável que também exerce influência no desempenho do processo de BRMS. Módulos com dois diferentes diâmetros foram testados (2,54 cm e 1,91 cm); o melhor resultado foi observado no módulo de maior diâmetro. A menor densidade de empacotamento resulta em um maior espaçamento entre as fibras, provocando uma aeração mais homogênea no interior do feixe de membranas. As duas geometrias de aeração testadas (Modo 1 e Modo 2) apresentaram resultados semelhantes de fluxo permeado, indicando que o Modo 2 de aeração não melhorou o desempenho do processo como se esperava. A maior homogeneidade de aeração no interior de feixe, a partir de aeradores construídos com as próprias fibras, não foi atingida, mostrando que um novo projeto de aeradores deve ser estudado. Em todas as condições hidrodinâmicas testadas, a eficiência do tratamento foi verificada, uma vez que a remoção de matéria orgânica para COT e DQO foi de 96% e 93%, respectivamente. Propriedades do permeado, como condutividade elétrica, pH e turbidez foram mensuradas, apresentando variações menores que as medidas do efluente, revelando a capacidade que o sistema apresenta em suportar as variações na corrente de alimentação. / The Membrane Bioreactor (MBR) process was developed in the late 1960. The system consists in a combination of biological process and membrane separation mechanism, and the advantages with respect of conventional treatment are the higher treatment efficiency and a smaller area of installation for the same treatment capacity. The main limitation of this process is the membrane fouling, in a way that air flow rate represents an important operating condition to prevent the fouling formation in Submerged Membrane Bioreactors (SMBR). In this sense, the aim of this work is to evaluate the effects of hydrodynamic conditions on process performance, such as air flow rate, packing density of the membrane module and aeration geometry. The system used consists in a pilot-scale SMBR, which operates at constant pressure and continuous mode during a period of 4 days. The modules were built with hollow fiber polymeric microfiltration membrane and the material is poly(ether)imide (PEI). For the three different air flow rates studied (2, 5 and 8 L.min-1), results showed there is a limit value for this parameter, in which above this value a better performance will not be obtained, even can be worse. The air flow rate of 5 L.min-1 presented the best performance, followed by 8 and 2 L.min-1. The module packing density study for two diameters (0.75 and 1 inch), the best result was observed in the larger diameter module, because lower packing density causes more space between fibres, increasing the aeration homogeneity inside de fibre bundle. Both aeration geometry tested showed similar permeate flows, indicating the different geometry used did not affect the performance process. The aerators constructed with the hollow fibers did not promote aeration homogeneity inside the bundle, and new aeration geometry must be projected. For all hydrodynamics conditions, the system treatment was efficient in removing organical matter, since the removal for TOC and COD was 96% and 93%, respectively. Permeate properties such as electrical conductivity, pH and turbidity measurements presented minor variations than effluent properties measurements, showing the system capacity to withstand with feed stream variations.

Thesis submitted in fulfilment of the requirements for the degree Doctor technologiae (engineering: chemical) In the faculty of engineering at the cape peninsula university of technology / Since the first uses of hollow-fiber membrane bioreactors (MBR’s) to immobilize whole cells were reported in the early 1970’s, this technology has been used in as wide ranging applications as enzyme production to bone tissue engineering. The potential of these devices in industrial applications is often diminished by the large diffusional resistances of the membranes. Currently, there are no analytical studies on the performance of the MBR which account for both convective and diffusive transport. The purpose of this study was to quantify the efficiency of a biocatalytic membrane reactor used for the production of enzymes. This was done by developing exact solutions of the concentration and velocity profiles in the different regions of the membrane bioreactor (MBR). The emphasis of this study was on the influence of radial convective flows, which have generally been neglected in previous analytical studies. The efficiency of the MBR was measured by means of the effectiveness factor. An analytical model for substrate concentration profiles in the lumen of the MBR was developed. The model was based on the solution of the Navier-Stokes equations and Darcy’s law for velocity profiles, and the convective-diffusion equation for the solute concentration profiles. The model allowed for the evaluation of the influence of both hydrodynamic and mass transfer operating parameters on the performance of the MBR. These parameters include the fraction retentate, the transmembrane pressure, the membrane hydraulic permeability, the Reynolds number, the axial and radial Peclet numbers, and the dimensions of the MBR. The significant findings on the hydrodynamic studies were on the influence of the fraction retentate. In the dead-end mode it was found that there was increased radial convective flow, and hence more solute contact with the enzymes/biofilm immobilised on the surface of the membrane. The improved solute-biofilm contact however was only limited to the entrance half of the MBR. In the closed shell mode there was uniform distribution of solute, however, radial convective flows were significantly reduced. The developed model therefore allowed for the evaluation of an optimum fraction retentate value, where both the distribution of solutes and radial convective flows could be maximised.

O processo de Biorreatores com Membranas (BRM) foi desenvolvido no final da década de 1960, consistindo em um sistema que associa o tratamento biológico de efluentes com o mecanismo de separação por membranas, e apresenta vantagens com relação ao tratamento convencional, tais como maior eficiência de tratamento e um menor espaço físico de instalação para a mesma capacidade de tratamento. O fenômeno de incrustação das membranas (em inglês, fouling) representa a principal limitação desse processo, de modo que uma das condições operacionais mais importantes na prevenção da incrustação em um sistema BRM Submerso (BRMS) é a vazão de aeração. Diante desta situação, o objetivo do trabalho consiste em avaliar os efeitos das condições hidrodinâmicas no desempenho do processo, tais como vazão de aeração, densidade de empacotamento do módulo de membranas e geometria dos aeradores. O sistema utilizado no trabalho consistiu em um BRMS automatizado, operando em pressão constante e de forma contínua, durante um período de 4 dias. Os módulos foram construídos com membranas poliméricas de microfiltração do tipo fibra oca, cujo material foi a poli(éter)-imida (PEI). Três diferentes vazões de aeração foram estudadas (2, 5 e 8 L.min-1), mostrando, a partir dos resultados, que existe uma vazão de aeração limite benéfica ao sistema e que, acima deste valor, um melhor desempenho não pode ser atingido, inclusive, podendo prejudicá-lo. Para o sistema de estudo, a vazão de 5 L.min-1 apresentou o melhor desempenho, seguido de 8 e 2 L.min-1. O estudo da densidade de empacotamento do módulo mostrou que esta é uma variável que também exerce influência no desempenho do processo de BRMS. Módulos com dois diferentes diâmetros foram testados (2,54 cm e 1,91 cm); o melhor resultado foi observado no módulo de maior diâmetro. A menor densidade de empacotamento resulta em um maior espaçamento entre as fibras, provocando uma aeração mais homogênea no interior do feixe de membranas. As duas geometrias de aeração testadas (Modo 1 e Modo 2) apresentaram resultados semelhantes de fluxo permeado, indicando que o Modo 2 de aeração não melhorou o desempenho do processo como se esperava. A maior homogeneidade de aeração no interior de feixe, a partir de aeradores construídos com as próprias fibras, não foi atingida, mostrando que um novo projeto de aeradores deve ser estudado. Em todas as condições hidrodinâmicas testadas, a eficiência do tratamento foi verificada, uma vez que a remoção de matéria orgânica para COT e DQO foi de 96% e 93%, respectivamente. Propriedades do permeado, como condutividade elétrica, pH e turbidez foram mensuradas, apresentando variações menores que as medidas do efluente, revelando a capacidade que o sistema apresenta em suportar as variações na corrente de alimentação. / The Membrane Bioreactor (MBR) process was developed in the late 1960. The system consists in a combination of biological process and membrane separation mechanism, and the advantages with respect of conventional treatment are the higher treatment efficiency and a smaller area of installation for the same treatment capacity. The main limitation of this process is the membrane fouling, in a way that air flow rate represents an important operating condition to prevent the fouling formation in Submerged Membrane Bioreactors (SMBR). In this sense, the aim of this work is to evaluate the effects of hydrodynamic conditions on process performance, such as air flow rate, packing density of the membrane module and aeration geometry. The system used consists in a pilot-scale SMBR, which operates at constant pressure and continuous mode during a period of 4 days. The modules were built with hollow fiber polymeric microfiltration membrane and the material is poly(ether)imide (PEI). For the three different air flow rates studied (2, 5 and 8 L.min-1), results showed there is a limit value for this parameter, in which above this value a better performance will not be obtained, even can be worse. The air flow rate of 5 L.min-1 presented the best performance, followed by 8 and 2 L.min-1. The module packing density study for two diameters (0.75 and 1 inch), the best result was observed in the larger diameter module, because lower packing density causes more space between fibres, increasing the aeration homogeneity inside de fibre bundle. Both aeration geometry tested showed similar permeate flows, indicating the different geometry used did not affect the performance process. The aerators constructed with the hollow fibers did not promote aeration homogeneity inside the bundle, and new aeration geometry must be projected. For all hydrodynamics conditions, the system treatment was efficient in removing organical matter, since the removal for TOC and COD was 96% and 93%, respectively. Permeate properties such as electrical conductivity, pH and turbidity measurements presented minor variations than effluent properties measurements, showing the system capacity to withstand with feed stream variations.

O processo de Biorreatores com Membranas (BRM) foi desenvolvido no final da década de 1960, consistindo em um sistema que associa o tratamento biológico de efluentes com o mecanismo de separação por membranas, e apresenta vantagens com relação ao tratamento convencional, tais como maior eficiência de tratamento e um menor espaço físico de instalação para a mesma capacidade de tratamento. O fenômeno de incrustação das membranas (em inglês, fouling) representa a principal limitação desse processo, de modo que uma das condições operacionais mais importantes na prevenção da incrustação em um sistema BRM Submerso (BRMS) é a vazão de aeração. Diante desta situação, o objetivo do trabalho consiste em avaliar os efeitos das condições hidrodinâmicas no desempenho do processo, tais como vazão de aeração, densidade de empacotamento do módulo de membranas e geometria dos aeradores. O sistema utilizado no trabalho consistiu em um BRMS automatizado, operando em pressão constante e de forma contínua, durante um período de 4 dias. Os módulos foram construídos com membranas poliméricas de microfiltração do tipo fibra oca, cujo material foi a poli(éter)-imida (PEI). Três diferentes vazões de aeração foram estudadas (2, 5 e 8 L.min-1), mostrando, a partir dos resultados, que existe uma vazão de aeração limite benéfica ao sistema e que, acima deste valor, um melhor desempenho não pode ser atingido, inclusive, podendo prejudicá-lo. Para o sistema de estudo, a vazão de 5 L.min-1 apresentou o melhor desempenho, seguido de 8 e 2 L.min-1. O estudo da densidade de empacotamento do módulo mostrou que esta é uma variável que também exerce influência no desempenho do processo de BRMS. Módulos com dois diferentes diâmetros foram testados (2,54 cm e 1,91 cm); o melhor resultado foi observado no módulo de maior diâmetro. A menor densidade de empacotamento resulta em um maior espaçamento entre as fibras, provocando uma aeração mais homogênea no interior do feixe de membranas. As duas geometrias de aeração testadas (Modo 1 e Modo 2) apresentaram resultados semelhantes de fluxo permeado, indicando que o Modo 2 de aeração não melhorou o desempenho do processo como se esperava. A maior homogeneidade de aeração no interior de feixe, a partir de aeradores construídos com as próprias fibras, não foi atingida, mostrando que um novo projeto de aeradores deve ser estudado. Em todas as condições hidrodinâmicas testadas, a eficiência do tratamento foi verificada, uma vez que a remoção de matéria orgânica para COT e DQO foi de 96% e 93%, respectivamente. Propriedades do permeado, como condutividade elétrica, pH e turbidez foram mensuradas, apresentando variações menores que as medidas do efluente, revelando a capacidade que o sistema apresenta em suportar as variações na corrente de alimentação. / The Membrane Bioreactor (MBR) process was developed in the late 1960. The system consists in a combination of biological process and membrane separation mechanism, and the advantages with respect of conventional treatment are the higher treatment efficiency and a smaller area of installation for the same treatment capacity. The main limitation of this process is the membrane fouling, in a way that air flow rate represents an important operating condition to prevent the fouling formation in Submerged Membrane Bioreactors (SMBR). In this sense, the aim of this work is to evaluate the effects of hydrodynamic conditions on process performance, such as air flow rate, packing density of the membrane module and aeration geometry. The system used consists in a pilot-scale SMBR, which operates at constant pressure and continuous mode during a period of 4 days. The modules were built with hollow fiber polymeric microfiltration membrane and the material is poly(ether)imide (PEI). For the three different air flow rates studied (2, 5 and 8 L.min-1), results showed there is a limit value for this parameter, in which above this value a better performance will not be obtained, even can be worse. The air flow rate of 5 L.min-1 presented the best performance, followed by 8 and 2 L.min-1. The module packing density study for two diameters (0.75 and 1 inch), the best result was observed in the larger diameter module, because lower packing density causes more space between fibres, increasing the aeration homogeneity inside de fibre bundle. Both aeration geometry tested showed similar permeate flows, indicating the different geometry used did not affect the performance process. The aerators constructed with the hollow fibers did not promote aeration homogeneity inside the bundle, and new aeration geometry must be projected. For all hydrodynamics conditions, the system treatment was efficient in removing organical matter, since the removal for TOC and COD was 96% and 93%, respectively. Permeate properties such as electrical conductivity, pH and turbidity measurements presented minor variations than effluent properties measurements, showing the system capacity to withstand with feed stream variations.