O potencial de aplicação do biofiltro aerado submerso (BF) para pós-tratamento de efluentes de um reator anaeróbio compartimentado foi avaliado através de um experimento em escala de laboratório (bancada), visando adequar o efluente tratado aos padrões estabelecidos pela legislação ambiental. Estudou-se a remoção de matéria orgânica e sólidos suspensos no BF, e também a possibilidade de nitrificação no reator. O reator foi construído em coluna de acrílico com 1,30 m de altura, 100 mm de diâmetro e com volume útil de 7,2 L, sendo operado com tempo de detenção hidráulica de 5 horas. Como suporte de imobilização celular, utilizou-se matrizes cúbicas de espuma de poliuretano. Neste trabalho, são apresentados os principais resultados obtidos na operação contínua do reator BF, durante 93 dias consecutivos, divididos em duas fases, devido à variação da carga orgânica volumétrica aplicada (Fase I: 0,99 - 1,87 kg DQO/m3. dia; Fase II: 0,26 - 0,88kg DQO/m3. dia). Durante a fase I de operação, o BF alcançou eficiências médias de remoção de DQO e DBO5 da amostra bruta de 82 e 86%, respectivamente, e de conversão do nitrogênio amoniacal de 81%, com concentração média efluente de 7,5 mg N-amoniacal/L. Na fase final de operação, para remoções médias de 70% de DQOB e 57% de DBO5, o efluente produzido pelo BF apresentava concentrações médias de 30 mg DQOB e 21 mg DBO5/L. Entretanto, o processo de nitrificação nessa fase foi instável, com concentração média de efluente de 25,3 mg N-amoniacal/L. O BF produziu efluente clarificado alcançando valores médios de 3,46 e 2,58 mg/L para SST e SSV, para segunda fase de operação. Este efluente atendeu ao padrão de lançamento do Estado de São Paulo em 100% dos resultados de DBO5, durante todo o período experimental, apresentando bom desempenho na remoção de matéria orgânica, tanto para altas como para baixas cargas orgânicas volumétricas aplicadas. A espuma de poliuretano mostrou-se um suporte adequado para imobilização da biomassa aeróbia e remoção de sólidos suspensos, devida a sua grande capacidade de absorção. Constatou-se, portanto, que o emprego do biofiltro aerado submerso apresenta-se como uma alternativa vantajosa como pós-tratamento de efluentes de reatores anaeróbios, produzindo efluente com excelente quantidade e parcialmente nitrificado. / The potential of application of the submerged aerated biofilter (BF) for post-treatment of effluents of an anaerobic baffed reactor was evaIuated through an experiment on Iaboratory scale to adapt the treated effluent to the established quality standards required by the environmental legislation. The removal of organic matter and suspended solids in BF, and aIso the possibility of nitrification in the reactor were studied. The reactor was a column of acrylic with 1,30 m of height, 100 mm diameter and with a useful volume of 7,2 L, being operated with hydraulic detention time of 5 hours. As a support for celluIar immobilization, cubic matrices of polyurethane foam. In this work, the main results were obtained in the continuous operation of the BF reactor, for 93 consecutive days, divided in two phases due to the variation of the applied organic volumetric loading rate (phase I: 0,99-1,87 kg COD/m3.day; Phase II: 0,26-0,88 kg COD/m3.day). During phase I of the operation, BF reached average removal efficiencies of COD and BOD5 of the raw samples of 82 and 86%, respectively, and of conversion of the ammonia nitrogen of 81%, with average effluent concentration of 7,5 mg N-ammonia/L. In the final phase of operation, for removals of 70% of COD and 57% of BOD5, the effluent produced by BF presented average concentrations of 30 mg COD/L and 21 mg BOD5/L. However, the nitrification process in that phase was unstable, with effluent concentrations of 25,3 mg N-ammonia/L. BF produced a very clarified effluent reaching average values of 3,46 and 2,58 mg/L for SST and SSV, for the second operation phase. This effluent satisfied the qualify standards for its discharge in a stream in the State of São Paulo in 100% of the results of BOD5, during the whole experimental period, presenting good performance in the removaI of organic matter, for high as well as for low organic volumetric loading applied. The polyurethane foam demonstrate to be an appropriate support for immobilization of the aerobic biomass and removaI of suspended solids, due to its great absorption capacity. It was found that the employment of the submerged aerated biofilter offers as an advantageous aIternative as anaerobic eftluent post-treatment, producing effluent with excellent quality and partially nitrified.

Este trabalho teve como finalidade a avaliação da viabilidade técnica e econômica da utilização do processo de ozonização seguido de biofiltro aerado submerso, para melhoria da qualidade de efluente de reator anaeróbio compartimentado, para atender a legislação ambiental no que se refere ao padrão de emissão e para o reúso. A pesquisa foi dividida em três etapas. Na primeira etapa avaliou-se a concentração de ozônio aplicada e o seu tempo de contato através de um planejamento experimental, composto por planejamento fatorial e metodologia de superfície de resposta. Na segunda etapa realizou-se ensaios de isotermas utilizados como critério de escolha para o tipo de carvão ativado granular utilizado como meio suporte do biofiltro aerado submerso. Na terceira etapa operou-se o sistema de pós-tratamento composto por ozônio - biofiltro aerado submerso para avaliação de sua eficiência e comparação com os padrões e critérios de reúso. Na primeira etapa foram encontradas duas condições de maior eficiência para dosagens de 10 mg O3/L em 30 minutos e 30 mg O3/L em 10 minutos. A segunda etapa ficou prejudicada em função do efluente ozonizado ter floculado, com isso interferindo no ensaio de isoterma. Na terceira etapa foram construídos dois biofiltros aerados submersos, um com meio suporte de carvão ativado granular e outro com cubos de espuma de poliuretano. Os dois BFs apresentaram efluente com excelente qualidade final. O BFs com meio suporte de CAG demonstrou ser o mais eficiente entre os dois, teve estabilização mais rápida e produziu efluente final com DQO da ordem de 14,3 mg/L e SST de 6,8 mg/L. O custo do pós-tratamento ficou em torno de R$ 0,25 por metro cúbico para população de 10.000 habitantes e de R$ 0,16 para população de 200.000 habitantes, demonstrando com isso que é um processo viável técnica e economicamente. O reúso agrícola torna-se interessante, visto que, o efluente final apresenta fósforo e nitrato que podem ser consumidos pelas plantas. / This work had as purpose the assessment of the technical and economical viability of ozonization process\' use followed by submerged aerated biofilter, for improvement of the quality of effluent of anaerobic baffed reactor, to attend the environmental legislation in what it refers to the emission pattern and reuse guidelines. The research was divided in three faces. In the first face it was evaluated the concentration of ozone applied and its time of contact through a factorial planning and response surface methodology. In the second face, tests of isotherms were made as choice criterion for the type of granulate activated carbon used as material support of the submerged aerated biofilter. In the third face the post-treatment system composed by ozone - submerged aerated biofilter was operated for assessment of your performance and a comparison with the patterns and reuse criteria. In the first face two conductions of greater performance were found: one with 10 mg O3/L and 30 min and other with 30 mg O3/L and 10 min. The second face was prejudiced in function of the effluent ozonizated to have floculated, with that interfering in the isotherm test. In the third faces two submerged aerated biofilters were built, one with granulate activated carbon and other with polyurethane foam as material supports. The BFs presented effluent with excellent final quality. The BFs with GAC demonstrated to be the most efficient among the two, it had faster stabilization and it produced final effluent with COD of the order of 14,3 mg/L and TSS of 6,8 mg/L. The cost of the post-treatment was around in R$ 0,25 for cubic meter for 10.000 persons and R$ 0,16 for 200.000 persons, demonstrating viable technique and economically of process. The agricultural reuse becomes interesting, because the final effluent presents phosphorus and nitrate that can be consumed by the plants.

O principal objetivo deste trabalho foi a avaliação da viabilidade do pós-tratamento de efluente rico em sulfato pré-tratado em sistema anaeróbio, explorando o processo de nitrificação e desnitrificação simultâneas (NDS), em reator de leito estruturado submetido a aeração intermitente (LEAI), utilizando sulfeto como doador de elétrons na redução do nitrogênio oxidado remanescente. O trabalho foi dividido em duas etapas, sendo o sulfeto (HS-) fornecido como doador de elétrons preferencial para desnitrificação. Na Etapa 1, HS- produzido pelas bactérias redutoras de sulfato (BRS) no reator anaeróbio (RAn) esteve continuamente presente no efluente encaminhado ao reator LEAI, uma vez que os dois sistemas foram operados em série. Como resultado, observou-se efeitos tóxicos sobre a comunidade nitrificante, limitando a remoção de N-total. A eficiência máxima de oxidação de N-NH4+ atingida foi de 60 ± 12%. Na Etapa 2, HS- passou a ser adicionado por bombeamento de solução concentrada de sulfeto de sódio. Duas estratégias de adição do sulfeto foram testadas, iniciadas após os 30 min iniciais de cada etapa não-aerada: solução de sulfeto adicionada em pulsos únicos, com tempo de bombeamento de 15 min (Estratégia I) e adição de maneira contínua ao longo dos 90 min restantes de cada fase não-aerada (Estratégia II). A forma de administração de sulfeto reduziu seu efeito inibitório à comunidade nitrificante na Etapa 2, alcançando eficiência de oxidação de N-NH4+ de 65 ± 7,8%. Entretanto, a remoção de N-total no reator LEAI foi limitada pela etapa de desnitrificação, uma vez que aporte de doador de elétrons inorgânico manteve-se abaixo da demanda estequiométrica nas duas estratégias de adição de sulfeto testadas. Observou-se que a adição de sulfeto mais diluída ao longo do tempo (Estratégia II) teve efeitos menos negativos à biota nitrificante na fase subsequente, refletindo em maior estabilidade e aumento da eficiência média de nitrificação de 59 para 65%, em comparação com a Estratégia I. Testes de perfis temporais de concentrações foram realizados ao final de cada etapa para elucidar a dinâmica e os efeitos do sulfeto sobre os processos combinados de nitrificação e desnitrificação. Observou-se que o sulfeto dissolvido foi efetivamente utilizado como doador de elétrons em ambas as Etapas Experimentais, resultando em cargas máximas de N-total removido de 0,095 e 0,065 kgN m-3d-1 nas Etapas 1 e 2, respectivamente. Ao final do período operacional, análises de sequenciamento do rRNA 16s detectaram sequências relacionadas a microrganismos nitrificantes do gênero Luteimonas, desnitrificantes heterotróficos (Thauera e Azoarcus) e autotróficos (Thiobacillus). Esses resultados demonstram que os processos de nitrificação e desnitrificação (autotrófica e heterotrófica) foram os envolvidos na remoção de nitrogênio no reator LEAI. / The present study evaluated the feasibility of the post-treatment of the effluent from an anaerobic system treating sulfate-rich wastewater. The post-treatment was based on simultaneous nitrification and sulfide-driven autotrophic denitrification of the remaining oxidized nitrogen using a structured-bed reactor subjected to recirculation and intermittent aeration (SBRRIA). This investigation was divided into two main sections (Stages 1 and 2), with the sulfide (HS-) supplied as the preferred electron donor for denitrification. In Stage 1, the HS- biologically produced by the sulfate-reducing bacteria (SRB) in the anaerobic reactor (ARn) was continuously provided in the SBRRIA feeding, as the two systems were operated in series. As a result, sulfide partially inhibited the nitrifying activity, limiting the overall nitrogen removal performance. The maximum NH4+-N oxidation efficiency reached was 60 ± 12%. In Stage 2, HS- was added in the SBBRIA by pumping a concentrated solution of sodium sulfide. Two strategies of sulfide addition were tested, both of them initiated after 30 min of each non-aerated period of the intermittent aeration cycle. In Strategy I, the sulfide solution was added by single pulses of 15 min in each non-aerated period. In Strategy II, a continuous sulfide addition during 90 min of each non-aerated period was tested. The sulfide-controlled addition reduced its inhibitory effect on the nitrifying community in Stage 2, resulting in an NH4+-N oxidation efficiency of 65 ± 7.8%. However, the Total-N removal was still limited by the denitrification, as the sulfide supply remained below the stoichiometric demand in both two strategies tested. Strategy II was less harmful for the nitrifying activity in the subsequent aerated period, reflecting in higher stability and increase of the NH4+-N oxidation efficiency from 59 to 65%, compared to Strategy I. At the end of each stage, temporal profiles were performed to elucidate the dynamics of sulfide and its impacts on combined processes. Dissolved sulfide was effectively used as an electron donor for autotrophic denitrification in both stages, resulting in maximum Total-N removed loads of 0.095 and 0.065 kgN m-3d-1 in Stages1 and 2, respectively. At the end of the operational period, rRNA 16S sequencing analysis detected sequences related to nitrifiers belonging to Luteimonas, heterotrophic (Thauera and Azoarcus) and autotrophic (Thiobacillus) denitrifiers. These results demonstrated that nitrification and denitrification (autotrophic and heterotrophic pathways) were likely in the processes involved in nitrogen removal in SBBRIA reactor.

Women treated for a gynecological cancer report longstanding post-treatment difficulties for which they rarely seek or receive help. Few intervention studies have successfully improved global sexual health within this population. Research in this domain is challenging due to inconsistent measurements of sexuality, low response rates and high attrition rates. The overarching study objectives were: (a) To contribute to the advancement of research on supportive care needs (including sexual health needs), desire for help, and predictors of needs; and, (b) To inform the development of services for gynecological cancer survivors. In Study 1, a qualitative interview study explored the experiences of 15 gynecological cancer survivors. Interviews were conducted and analysed based on the Interpretive Description approach . In Study 2 (for which results were analyzed in two parts), a descriptive, cross-sectional needs assessment was conducted to measure supportive care needs, desire for help, sexual health and vaginal changes, and service format preferences in 113 patients. In Part 1 of Study 2, descriptive and regression analyses explored patient needs, desire for help and potential predictors of these variables. In Part 2, a descriptive analysis explored sexual health needs and vaginal changes, desire for help with sexual health needs, and their associations with sociodemographic and medical variables. Qualitative results from Study 1 suggested that psychological, emotional and relational aspects of sexuality were as important to the participants as physiological sexual response. In the needs assessment, the strongest predictors of greater unmet needs and increased readiness for help were younger age and shorter time since treatment. Moderate to high sexual and social needs were equally prevalent in women recently treated and those treated several years prior to the study, suggesting that sexual and social needs may remain unaddressed over time. Further, many women who reported a need did not desire help, demonstrating the subjectivity of needs and distress, as well as the potential presence of barriers to seeking help. Both studies revealed a common finding, where sexual health needs were a product of the discordance between participants’ current sexual experiences and their perceptions of ideal sexual health. Overall, the two studies indicate that a significant subgroup of patients experience unmet needs in cancer survivorship, most of which are non-physical; also, while some needs were higher following treatment, unmet social and sexual health needs show little relationship with time since treatment. Ambivalence about receiving help with unmet needs is related to beliefs about the role of the health care team in meeting non-physical needs, as well as other perceived barriers. Patient’s perceived sexual health needs and barriers to receiving help should be evaluated within a comprehensive framework of needs and discussed one-on-one. Future research should explore the added predictive value of other groups of medical and psychological variables.

This study primarily investigated factors which impact abstaining from drugs for adolescent men after finishing treatment at a specific treatment center in Sweden. The method chosen for this essay was quantitative, using surveys sent to males that finished a treatment period of a minimum time of 4 months at this therapeutic community. Of the 83 questionnaires that were originally sent, 23 responded. Further, the empirical data was tested in the computer program SPSS using gamma and lambda tests obtaining results for the factors to determine whether they correlated with one another other. The essay is based upon the theoretical framework of the salutogenic perspective, systems theory and therapeutic alliance theory. During this study results showed that factors such as relocation, post treatment programs were effective for the dis-continued use of drugs.

Made available in DSpace on 2014-06-11T19:32:54Z (GMT). No. of bitstreams: 0 Previous issue date: 2010-02-24Bitstream added on 2014-06-13T20:24:21Z : No. of bitstreams: 1 duda_rm_dr_jabo.pdf: 7705565 bytes, checksum: 22edf4cc4e57fedc9fa2426e83e181e0 (MD5) / Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP) / Avaliou-se o desempenho de um reator anaeróbio de fluxo ascendente com manta de lodo (UASB) seguido de um filtro anaeróbio de fluxo ascendente, instalados em série, com volume total de 300 L e 190 L, respectivamente, no tratamento de águas residuárias de suinocultura. As cargas orgânicas volumétricas aplicadas no reator UASB foram de 9,2 a 26,7 g DQOtotal (L d)-1. Para o pós-tratamento do efluente do sistema de tratamento anaeróbio utilizou-se um filtro biológico percolador (FBP) com volume total de 250 L. O meio suporte utilizado no filtro anaeróbio e no FBP foi composto por anéis de bambu e anéis de eletroduto plástico corrugado. As cargas hidráulicas superficiais (Qs) aplicadas no FBP variaram de 3,5 a 21,1 m3 (m2 d)-1. Os tempos de detenção hidráulica (TDH) aplicados no sistema de tratamento anaeróbio e pós-tratamento foram de 23,3 a 66,6 h. As produções volumétricas de metano no sistema de tratamento anaeróbio variaram de 0,16 a 0,68 L CH4 (L reator d)-1. Foram observadas eficiências médias de remoção de até 97% para a demanda química de oxigênio total, de 98% para os sólidos suspensos totais, de 78% para o nitrogênio total, de 79% para o fósforo total, de 99,9% para o cobre, de 99,9% para o zinco e de 99,99% para os coliformes termotolerantes, no sistema de tratamento anaeróbio e póstratamento. Com a utilização de diferentes fontes de substrato no ensaio de atividade da microbiota, observou-se o crescimento equilibrado das populações hidrolíticas, acidogênicas, acetogênicas e metanogênicas acetoclásticas e hidrogenotróficas no lodo dos reatores anaeróbios. Com a aplicação da técnica de biologia molecular (metagenômica) foram identificadas no lodo do reator UASB e do filtro anaeróbio de fluxo ascendente arquéias metanogênicas das famílias Methanomicrobiaceae, Methanobacteriacea, Methanosaetaceae e Methanosarcinaceae. / The performance of an upflow anaerobic sludge blanket (UASB) followed of the anaerobic filter, installed in series, were evaluated for the treatment of swine wastewater. The total volume of UASB and anaerobic filter were of 300 L and 190 L, respectively. The organic load rate applied on the reactor UASB were of 9.2 to 26.7 g total COD (L d)-1, in the start and assays 1, 2, 3 and 4. For the post-treatment of effluent the anaerobic system was used a trickling filter, with total volume of 250 L. The supports used in the anaerobic filter and trickling filter were composed by bamboo rings in the start up and assays 1 to 2 and plastics rings in the assays 3 to 4. The hydraulic load applied on the trickling filter were of 3.5 to 21.1 m3 (m2 d)-1. The hydraulic detetion time (HDT) applied of system anaerobic and post treatment were 23.3 at 66.6 h. The volumetric methane productions ranged from 0.16 a 0.68 L CH4 (L reactor d)-1. The efficiencies of removal the chemical oxygen demand, total solids suspended, copper, zinc and fecal coliforms were of up to 97, 98, 78, 79, 99.9, 99.9 e 99.99%, respectively, for the anaerobic and post-treatment. With the use of different substratum sources in the assays of specific methanogenic activity, it was observed the balanced growth of the populations of microorganisms in the sludge of anaerobic reactor. The archaeas of the families Methanomicrobiaceae, Methanobacteriaceae; Methanosaetaceae and Methanosarcinaceae were identified in the sludge of the reactor UASB and of the anaerobic filter.

Orientador: Roberto Alves de Oliveira / Banca: Eugênio Foresti / Banca: Maria Bernadete Amâncio Varesche / Banca: Manoel Victor Franco Lemos / Banca: Edson Aparecido Abdul Nour / Resumo: Avaliou-se o desempenho de um reator anaeróbio de fluxo ascendente com manta de lodo (UASB) seguido de um filtro anaeróbio de fluxo ascendente, instalados em série, com volume total de 300 L e 190 L, respectivamente, no tratamento de águas residuárias de suinocultura. As cargas orgânicas volumétricas aplicadas no reator UASB foram de 9,2 a 26,7 g DQOtotal (L d)-1. Para o pós-tratamento do efluente do sistema de tratamento anaeróbio utilizou-se um filtro biológico percolador (FBP) com volume total de 250 L. O meio suporte utilizado no filtro anaeróbio e no FBP foi composto por anéis de bambu e anéis de eletroduto plástico corrugado. As cargas hidráulicas superficiais (Qs) aplicadas no FBP variaram de 3,5 a 21,1 m3 (m2 d)-1. Os tempos de detenção hidráulica (TDH) aplicados no sistema de tratamento anaeróbio e pós-tratamento foram de 23,3 a 66,6 h. As produções volumétricas de metano no sistema de tratamento anaeróbio variaram de 0,16 a 0,68 L CH4 (L reator d)-1. Foram observadas eficiências médias de remoção de até 97% para a demanda química de oxigênio total, de 98% para os sólidos suspensos totais, de 78% para o nitrogênio total, de 79% para o fósforo total, de 99,9% para o cobre, de 99,9% para o zinco e de 99,99% para os coliformes termotolerantes, no sistema de tratamento anaeróbio e póstratamento. Com a utilização de diferentes fontes de substrato no ensaio de atividade da microbiota, observou-se o crescimento equilibrado das populações hidrolíticas, acidogênicas, acetogênicas e metanogênicas acetoclásticas e hidrogenotróficas no lodo dos reatores anaeróbios. Com a aplicação da técnica de biologia molecular (metagenômica) foram identificadas no lodo do reator UASB e do filtro anaeróbio de fluxo ascendente arquéias metanogênicas das famílias Methanomicrobiaceae, Methanobacteriacea, Methanosaetaceae e Methanosarcinaceae. / Abstract: The performance of an upflow anaerobic sludge blanket (UASB) followed of the anaerobic filter, installed in series, were evaluated for the treatment of swine wastewater. The total volume of UASB and anaerobic filter were of 300 L and 190 L, respectively. The organic load rate applied on the reactor UASB were of 9.2 to 26.7 g total COD (L d)-1, in the start and assays 1, 2, 3 and 4. For the post-treatment of effluent the anaerobic system was used a trickling filter, with total volume of 250 L. The supports used in the anaerobic filter and trickling filter were composed by bamboo rings in the start up and assays 1 to 2 and plastics rings in the assays 3 to 4. The hydraulic load applied on the trickling filter were of 3.5 to 21.1 m3 (m2 d)-1. The hydraulic detetion time (HDT) applied of system anaerobic and post treatment were 23.3 at 66.6 h. The volumetric methane productions ranged from 0.16 a 0.68 L CH4 (L reactor d)-1. The efficiencies of removal the chemical oxygen demand, total solids suspended, copper, zinc and fecal coliforms were of up to 97, 98, 78, 79, 99.9, 99.9 e 99.99%, respectively, for the anaerobic and post-treatment. With the use of different substratum sources in the assays of specific methanogenic activity, it was observed the balanced growth of the populations of microorganisms in the sludge of anaerobic reactor. The archaeas of the families Methanomicrobiaceae, Methanobacteriaceae; Methanosaetaceae and Methanosarcinaceae were identified in the sludge of the reactor UASB and of the anaerobic filter. / Doutor

Made available in DSpace on 2014-06-11T19:27:22Z (GMT). No. of bitstreams: 0 Previous issue date: 2009-08-10Bitstream added on 2014-06-13T20:16:34Z : No. of bitstreams: 1 santos_ac_me_jabo.pdf: 2357679 bytes, checksum: 9aae6927779549a378163bb987c18730 (MD5) / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) / Avaliou-se o desempenho de um sistema combinado anaeróbioaeróbio para o tratamento de águas residuárias de suinocultura, com concentrações médias de sólidos suspensos totais (SST) de 18624, 11395, 6690 e 21705 mg L-1. Foram utilizados quatro reatores anaeróbios horizontais com volume total de 49,5 L cada, um com manta de lodo (RAHML) e três de leito fixo (RAHLF), instalados em série e seguidos de um reator aeróbio operado em bateladas alimentadas sequenciais (RBS, com alimentação contínua). Nos RAHLF foram utilizados como meios suporte anéis de bambu, anéis plásticos de eletroduto corrugado e anéis de bucha (Luffa cillyndrica), respectivamente. Os tempos de detenção hidráulica (TDH) e as cargas orgânicas volumétricas (COV) aplicadas no RAHML foram de 12, 10, 8 e 8 h e 52,6; 60,9; 64,8 e 123,2 g DQO (L d)-1, respectivamente. O RBS foi operado com ciclo de 24 h e COV de 0,34; 0,50; 0,32 e 3,88 g DQO (L d)-1. As eficiências médias de remoção de DQOtotal e SST no conjunto de reatores anaeróbios horizontais, em série, diminuíram de 95,5 a 96,7% para 78,8%, e de 95,0 a 98,7% para 85,6% respectivamente, com o aumento da COV para 123,2 g DQO (L d)-1 no RAHML. As maiores produções de metano ocorreram nos RAHLF com valores médios de até 0,925 m3 CH4 (m3 reator d)-1 e 0,31 m3 CH4 (g DQO removida)-1 . A inclusão do RBS permitiu melhorar a qualidade do efluente e a estabilidade do sistema de tratamento, atingindo eficiências de remoção de DQOtotal de 94,2 a 99,0% e de SST de 94,4 a 99,3%. As eficiências médias de remoção de K, Ca, Mg e Na no sistema de tratamento foram de 50 a 81%, de 67 a 89 % de 65 a 79% e de 53 a 68%, respectivamente, e de Cu, Fe, Mn e Zn foram maiores, de 97 a 98%, de 63 a 99%, de 75 a 85% e de 89 a 94%, respectivamente, e podem ser atribuídas à imobilização no lodo. / An anaerobic-aerobic combined system performance was evaluated in swine water waste treatment with an average total suspended solids (TSS) concentration from 18624, 11395, 6690 and 21705 mg L-1, constituted by four horizontal anaerobic reactors each one having a total volume of 49.5 L, one of control-sludge (RAHML), and tree of fixed film installed in series (RAHLF), followed by a sequential operated batch reactor (ASBR) with continue feeding with total volume of 339 L. In the RAHLF was used of bamboo were used as support to fix the film, plastic rings, and wad (Luffa cillyndrica) rings. The hydraulic detention timing (HDT) and volumetric organic loads (VOL) applied in RAHML were 12, 10, 8 and 8 h of 52.6, 60.9, 64.8 and 123.2 g COD (Ld)-1 and the RBS operated in a 24-hours operational cycle were 0.34, 0.50, 0.32 and 3.88 g COD (L d)-1, into the assays number 1, 2, 3 and 4 respectively. The total COD and medium SST removed efficiently horizontal reactors set in serie, were from 95.5 to 96.7%, for 78.8 % and from 95 to 98.7% for 85.6% respectively. Increasing (VOL) to 123,2 g COD (L d)-1 in the (RAHLF). The higher methane production happened in RAHLF with medial values up to 0.925 m3 CH4 and 0.31 m3 CH4 (g COD removed). The ASBR inclusion enabled obtain COD removing efficiency in suspended solid from 94.2 a 99% and from 94.4 a 99.3% respectively. The K, Ca, Mg and Na medium removed efficiently in system were from 50 for 81% and 67 for 89%, 65 for 79% and 53 for 68%, for Cu, Fe, Mn and Zn medium removed efficiently in system were high from 97 for 98% and 63 for 99%, and 75 for 85% and 89 for 94%, respectively, and can be attributed to the sludge immobilization.

Made available in DSpace on 2015-05-07T14:49:38Z (GMT). No. of bitstreams: 1 arquivototal.pdf: 1400231 bytes, checksum: fb9f24d41beb924c130d174f918f19f8 (MD5) Previous issue date: 2005-12-20 / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / The objective of this thesis is to evaluate the performance of anaerobic filter with baffles (FAC) for the post treatment of anaerobic effluent and using rings cut from PET bottles as filling medium. The experiment was carried out in three phases characterized by the hydraulic retention times of 7, 9 and 10 days, respectively. The analysis of the UASB and FAC effluents was carried out weekly to evaluate the removal efficiency of organic material expressed as BOD5 e COD, solids and its different fractions, nutrients (nitrogen and phosphorus) and indicators of faecal contamination (thermotolerant Coliforms). The results showed that there were no significant differences between the FAC effluent during the three phases with respect to organic material and suspended solids (at 5% significance level), but there were differences in the electric conductivity, nitrogen and thermotolerant Coliforms. The FAC presented good performance of organic material removal (65% for COD and 64% for BOD5 during the first phase) and suspended solids (81% for TSS and 83% for VSS during the first phase). Thus it can be noted that the FAC presented good post treatment efficiency of anaerobic effluents, resulting in clarified effluent with low concentrations of organic material (12mg BOD5.L-1), suspended solids (<10 mg TSS. L-1) and turbidity (<10 UNT). With respect to sanitary quality the produced effluent had concentrations of thermotolerant in the range of 103 to 104 UFC.100 mL-1, hence above the standards established by the WHO (1989) for utilization in irrigation without restrictions. / O presente trabalho teve como objetivo avaliar o desempenho de filtro anaeróbio de chicanas (FAC) no pós-tratamento de efluente anaeróbio, usando garrafas PET como material de enchimento. O experimento foi realizado em três fases, delimitado pelos três tempos de detenção hidráulicas, 7, 9 e 10 dias, respectivamente. As análises dos efluentes do reator UASB e do FAC foram realizadas semanalmente, averiguando a remoção de matéria orgânica na forma de DBO5 e DQO, sólidos e suas frações, nutrientes (nitrogênio e fósforo) e indicadores de contaminação fecal (coliformes termotolerantes). Os resultados mostraram que não ocorreram diferenças significativas no efluente do FAC entre as três fases, em relação a matéria orgânica e sólidos (ao nível de 5%), mas houve diferença quanto a condutividade elétrica, nitrogênio e coliformes termotolerantes. O FAC apresentou bom desempenho quanto à remoção de matéria orgânica (65% para DQO e 64% para DBO5 durante a 1ª fase) e sólidos suspensos (81% para SST e 83% para SSV durante a 1ª fase). Diante desses resultados, observa-se que o FAC apresentou boa eficiência no pós-tratamento de efluente anaeróbio resultando em um efluente clarificado com baixas concentrações de matéria orgânica (12mg DBO5.L-1), sólidos suspensos (<10 mg SST. L-1) e turbidez (<10 UNT). Com relação à qualidade sanitária, o efluente produzido apresentava concentrações de coliformes termotolerantes variando de 103 a 104 UFC.100 mL-1, portanto valores acima dos padrões estabelecidos pelo OMS (1989) para ser utilizado em irrigação irrestrita.

Orientador: Roberto Alves de Oliveira / Banca: Egenio Foresti / Banca: Maria Bernadete Amâncio Varesche / Banca: Wanderley José de Melo / Banca: Edson Aparecido Abdul Nour / Resumo: Neste trabalho avaliou-se o desempenho de sistema de tratamento combinado anaeróbio-aeróbio constituído por dois reatores anaeróbios de fluxo ascendente com manta de lodo (UASB), em série, em escala piloto (volumes de 510 e 209 L, respectivamente) seguidos de um reator em batelada seqüencial (RBS - volume de trabalho 210 L) aeróbio, tratando águas residuárias de suinocultura com concentrações médias de sólidos suspensos totais (SST) variando de 5 a 11 g L-1 e submetidos a tempos de detenção hidráulica (TDH) de 28 e 14 h no primeiro reator (R1), 11 e 6 h no segundo reator (R2) e de 58 e 26 h no RBS. As eficiências médias de remoção de DQO total e SST variaram de 54 a 90% e de 54 a 96%, respectivamente, no conjunto de reatores UASB em dois estágios (R1+R2), com carga orgânica volumétrica (COV) de 11 a 26 g DQO (L d)-1 no R1. A produção volumétrica máxima de metano de 1,613 m3 CH4 (m3 reator d)-1 ocorreu no R1, com COV de 19 g DQO (L d)-1 e TDH de 14 h. No RBS aeróbio, como pós-tratamento do efluente gerado nos reatores UASB, as eficiências médias de remoção foram 89%, 93%, 61%, 89% e 71% para a DQO total, SST, P-total, NTK e NT, respectivamente, com COV variando de 0,4 a 3,6 g DQO (L d)-1. Assim, no sistema de tratamento combinado anaeróbio-aeróbio (R1+R2+RBS), as eficiências médias de remoção da DQO total, SST, P-total, NTK e NT atingiram valores de 96 a 99%, 96 a 99%, 77 a 85%, 76 a 97% e 68 a 89%, respectivamente, e dos micronutrientes de 77 a 98%, 94 a 99%, 83 a 97% e de 62 a 99% para Fe, Zn, Cu e Mn, respectivamente, Para os coliformes termotolerantes, as eficiências de remoção médias foram de 93,80 a 99,99%, obtendo-se valores mínimos de 2,3 x 103 NMP/100 mL. A atividade metanogênica específica do lodo dos reatores UASB foi mais elevada quando se utilizou o propionato + butirato como fonte de substrato, e quando os reatores foram operados... (Resumo completo, clicar acesso eletrônico abaixo) / Abstract: In this work a combination between aerobic and anaerobic treatment systems constituted by two Upflow Anaerobic Sludge Reactor (UASB) in series, in a pilot scale (510 and 209 L volume each respectively) followed by a sequential batch reactor (SBR - 210L net volume) aerobic, treating swine residual water having from 5 to 11 g L-1 of Total Suspended Solids (TSS) and under a hydraulic detention timing (HDT) of 28 and 14 hours in the first reactor (R1), 11 and 6 hours in the second reactor (R2) and 58 and 26 hours in the Sequential Batch Reactor (RBS). The COD and TSS average efficiency varied from 54 to 90% and from 54 to 96% respectively in the UASB two stages (R1 and R2), in a volumetric organic load (VOL) varying from 11 to 26g COD (L d)-1 in the R1. The maximum methane volumetric production was 1.613 m3 CH4 (m3 reactor d)-1 in the R1, having a 19g COD (L d)-1 and an HDT of 14h. Using an aerobic SBR as an effluent pretreater that was generate in the UASB reactors, it was reached an average of removing efficiency of 89%, 93%, 61%, 89% and 71% to total COD, TSS, total P, TNK and TN, respectively, COD varying from 0.4 to 3.6 g COD (L d)-1. This way, in the anaerobic-aerobic combined system (R1 + R2 + RBS) the total COD, TSS, total P, TNK and TN, average removing reached values from 96 to 99%, 96 to 99%, 77 to 85%, 76 to 97% and 68 to 89%, respectively. To Fe, Zn, Cu and Mn the average efficiency was from 77 to 98%, 94 to 99%, 83 to 97% and 62 to 99%, respectively. To the thermotolerant coliforms the removal efficiency average was from 93.80 to 99.99% reaching the lower value of 2.3 x 103 MPN/100 mL. The sludge specific methanogenic activity in the UASB reactors was more elevated when was used the propionate + butyrate as substrate in conjunction with the operation of 28 HDT, 11h and TSS affluent around 5 g L-1, reaching 0.443 and 0.206 mmol CH4 (g SV h)-1 in the reactors R1 and R2, respectively. / Doutor