Desempenho de sistema composto por reatores anaeróbios em série seguido de filtro biológico percolador no tratamento de águas residuárias de suinocultura
Carregando...
Arquivos
Data
2010-02-24
Autores
Duda, Rose Maria [UNESP]
Título da Revista
ISSN da Revista
Título de Volume
Editor
Universidade Estadual Paulista (Unesp)
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.
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.
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.
Descrição
Palavras-chave
Aguas residuais, Atividade metanogênica, Arquéias metanogênicas, Carga orgânica volumétrica, Specific methanogenic activity, Organic load rate, Anaerobic digestion, Nutrients, Post-treatment
Como citar
DUDA, Rose Maria. Desempenho de sistema composto por reatores anaeróbios em série seguido de filtro biológico percolador no tratamento de águas residuárias de suinocultura. 2010. xxviii, 241 f. Tese (doutorado) - Universidade Estadual Paulista, Faculdade de Ciências Agrárias e Veterinárias, 2010.