Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino

Detalhes bibliográficos
Ano de defesa: 2012
Autor(a) principal: Guerra, Alaine de Brito lattes
Orientador(a): Ceballos, Beatriz Suzana Ovruski de lattes
Banca de defesa: Aquino, Sérgio Francisco de lattes, Lopes, Wilton Silva
Tipo de documento: Dissertação
Tipo de acesso: Acesso aberto
Idioma: por
Instituição de defesa: Universidade Estadual da Paraíba
Programa de Pós-Graduação: Programa de Pós-Graduação em Ciência e Tecnologia Ambiental - PPGCTA
Departamento: Tecnologia Ambiental
Pró-Reitoria de Pós-Graduação e Pesquisa - PRPGP
País: BR
Palavras-chave em Português:
Palavras-chave em Inglês:
Área do conhecimento CNPq:
Link de acesso: https://repositorio.uepb.edu.br/handle/123456789/72194
Resumo: Usually, conventional water purification technology with eutrophic waters (high density of cyanobacteria and dissolved toxins) does not guarantee that the water produced is within the maximum allowable concentration of 1.0 µg/L of microcystin (Decree 2914/2011). Additional processes are needed, and the use of activated carbon is considered effective to reduced or eliminate those toxins. The present study aimed to evaluate in a bench-scale the removal of microcystin-LR in water supplies using conventional treatment followed by adsorption with granular activated carbon. The experiment was conducted in two stages. In the first stage coagulation assays were performed with the evaluation of five coagulants (with and without the use of polymers as auxiliaries) in order to select the most appropriate coagulant and its concentration to the water under investigation. The second stage were coagulation / flocculation tests and sedimentation using the conditions defined in the first step with raw water with an addition of a defined concentration of microcystin-LR extract. The extracted was obtained from the culture of a toxigenic strain of Microcystis aeruginosa. The final effluent was decanted in the jar test and stored. Two peristaltic pumps adduced the reserved water to the sand filters; the sand filter effluent was distributed to two columns of granular activated carbon with different particle size (0.42 to 1.40 and 0.60 to 2.36 mm). The results of coagulation assays showed the best results of removal of apparent color, turbidity, phytoplankton and particular true color, which is a strong competitor for the adsorption sites of activated carbon, with the polyaluminum chloride (dosage of 9.92 mg L -1 of Al 3 + and pH between 5 and 6, without the addition of alkalizing or acidifying). The conventional treatment steps were not efficient for microcystin-LR removal while the granular activated carbon from coconut showed high percentages of removal (80 to 100%). Although no statistically significant differences were observed in the removal of MC-LR between the different particle size, the had breakthrough coal to the smaller particle size (CC2) occurred in a shorter contact time (2 hours) which eventually reflected in a lower qe (2.1 µg/g) and a higher rate of use (8.09 gCAG / Lwater) when compared to the smaller particle size (CC1) that showed the best performance both in terms of qe (8.9 µg/g) as the rate use of (1.93 gCAG / Lwater) confirming its use in actual scale, since it ensures an effluent concentration below the Decree 2914/11 for a longer time and using a smaller quantity of coal.
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spelling 2015-09-25T12:19:59Z2026-02-25T12:48:41Z2012-11-302012-05-30GUERRA, Alaine de Brito. . 2012. 98 f. Dissertação (Mestrado em Tecnologia Ambiental) - Universidade Estadual da Paraíba, Campina Grande, 2012.https://repositorio.uepb.edu.br/handle/123456789/7219424004014005P9Usually, conventional water purification technology with eutrophic waters (high density of cyanobacteria and dissolved toxins) does not guarantee that the water produced is within the maximum allowable concentration of 1.0 µg/L of microcystin (Decree 2914/2011). Additional processes are needed, and the use of activated carbon is considered effective to reduced or eliminate those toxins. The present study aimed to evaluate in a bench-scale the removal of microcystin-LR in water supplies using conventional treatment followed by adsorption with granular activated carbon. The experiment was conducted in two stages. In the first stage coagulation assays were performed with the evaluation of five coagulants (with and without the use of polymers as auxiliaries) in order to select the most appropriate coagulant and its concentration to the water under investigation. The second stage were coagulation / flocculation tests and sedimentation using the conditions defined in the first step with raw water with an addition of a defined concentration of microcystin-LR extract. The extracted was obtained from the culture of a toxigenic strain of Microcystis aeruginosa. The final effluent was decanted in the jar test and stored. Two peristaltic pumps adduced the reserved water to the sand filters; the sand filter effluent was distributed to two columns of granular activated carbon with different particle size (0.42 to 1.40 and 0.60 to 2.36 mm). The results of coagulation assays showed the best results of removal of apparent color, turbidity, phytoplankton and particular true color, which is a strong competitor for the adsorption sites of activated carbon, with the polyaluminum chloride (dosage of 9.92 mg L -1 of Al 3 + and pH between 5 and 6, without the addition of alkalizing or acidifying). The conventional treatment steps were not efficient for microcystin-LR removal while the granular activated carbon from coconut showed high percentages of removal (80 to 100%). Although no statistically significant differences were observed in the removal of MC-LR between the different particle size, the had breakthrough coal to the smaller particle size (CC2) occurred in a shorter contact time (2 hours) which eventually reflected in a lower qe (2.1 µg/g) and a higher rate of use (8.09 gCAG / Lwater) when compared to the smaller particle size (CC1) that showed the best performance both in terms of qe (8.9 µg/g) as the rate use of (1.93 gCAG / Lwater) confirming its use in actual scale, since it ensures an effluent concentration below the Decree 2914/11 for a longer time and using a smaller quantity of coal.Usualmente, a potabilização de águas eutrofizadas com alta densidade de cianobactérias e toxinas dissolvidas pela tecnologia convencional não garante que a água produzida esteja dentro dos valores máximos permissíveis de 1,0 µg/L de microcistina (Portaria 2914/2011). Processos adicionais são necessários, e o uso de carvão ativado é considerado medida eficaz na solução deste problema. Neste contexto, o presente trabalho teve como objetivo principal avaliar em escala de bancada a remoção de microcistina-LR em água para abastecimento, utilizando tratamento convencional seguido de adsorção por carvão ativado granular. O experimento foi realizado em duas etapas. Na primeira, foram realizados ensaios de coagulação com avaliação de cinco coagulantes (com e sem o emprego de polímeros como auxiliares) para o estabelecimento do mais apropriado para a água em estudo. Na segunda etapa, foram realizados ensaios de coagulação/floculação e sedimentação de acordo com as condições definidas na etapa supracitada, utilizando água bruta com adição de uma concentração definida de extrato de microcistina-LR proveniente do cultivo de Microcystis aeruginosa. O efluente final decantado nos jarros do jar test foi armazenado, e em seguida aduzido a filtros de areia cujo efluente se distribuía para duas colunas de carvão ativado granular de diferentes granulometrias (0,42 - 1,40 e 0,60 - 2,36 mm). Os resultados dos ensaios de coagulação mostraram que o cloreto de polialumínio, na dosagem de 9,92 mg.L-1 de Al 3+e pH entre 5 e 6 (sem adição de alcalinizante ou acidificante), apresentou os melhores resultados em termos de remoção da cor aparente, turbidez, fitoplâncton e em especial da cor verdadeira que se apresenta como forte competidora pelos sítios de adsorção do carvão ativado. As etapas que compõem o tratamento convencional se mostraram pouco eficientes na remoção da microcistina-LR, enquanto que o carvão ativado granular de casca de coco apresentou elevados percentuais de remoção (entre 80 a 100%). Apesar de não ter sido observada diferenças estatisticamente significativas na remoção da MC-LR entre as diferentes granulometrias, o transpasse no carvão de maior granulometria (CC2) ocorreu em um menor tempo de contato (2 horas) o que acabou refletindo em um menor qe(2,1 µg/g) e uma maior taxa de uso (8,09gCAG/Lágua) quando comparado ao de menor granulometria (CC1) que apresentou melhor desempenho tanto em relação ao qe(8,9 µg/g) como pela taxa de uso de (1,93gCAG/Lágua) confirmando seu uso em escala real, uma vez que garante um efluente com concentração inferior ao que estabelece a Portaria 2914/11 por mais tempo e utilizando uma menor quantidade de carvão.Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - CAPESapplication/pdfUniversidade Estadual da ParaíbaPrograma de Pós-Graduação em Ciência e Tecnologia Ambiental - PPGCTAUEPBBRTecnologia AmbientalPró-Reitoria de Pós-Graduação e Pesquisa - PRPGPWater TreatmentCyanobacteriaCyanotoxinsActivated carbonCNPQTratamento de águaCianobactériasCianotoxinasCarvão ativadoAvaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestinoAssessment of health services and quality of life for diabetics during the Covid-19 pandemicinfo:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/masterThesisLibânio, Marcelohttp://lattes.cnpq.br/5168671769851394Aquino, Sérgio Francisco dehttp://lattes.cnpq.br/8758653660694681Lopes, Wilton SilvaCeballos, Beatriz Suzana Ovruski dehttp://lattes.cnpq.br/9321950498637802http://lattes.cnpq.br/0065347070645012Guerra, Alaine de Britoinfo:eu-repo/semantics/openAccessporreponame:Repositório Institucional da Universidade Estadual da Paraíba (UEPB)instname:Universidade Estadual da Paraíba (UEPB)instacron:UEPBORIGINALAlaine de Brito Guerra.pdfapplication/pdf1787696https://repositorio.uepb.edu.br/bitstreams/1a0e03af-4774-4da7-b64c-468232245762/download6bd0b35ebf464af75d4afd011fb94e39MD51trueAnonymousREADTHUMBNAILAlaine de Brito Guerra.pdf.jpgAlaine de Brito Guerra.pdf.jpgGenerated Thumbnailimage/jpeg3466https://repositorio.uepb.edu.br/bitstreams/110da636-4d59-4428-8ad8-42659d67df8c/downloada6b554836bf87684bf564b5d952d9a8aMD52falseAnonymousREADLICENSElicense.txtlicense.txttext/plain; charset=utf-81324https://repositorio.uepb.edu.br/bitstreams/eb7ab5c8-9493-42a6-876e-dc524f6330d5/downloadea12793326f265c7d8ea2bcdd2c49d6fMD53falseAnonymousREAD123456789/721942026-05-06T11:50:22.046210Zopen.accessoai:repositorio.uepb.edu.br:123456789/72194https://repositorio.uepb.edu.brRepositório InstitucionalPUBhttp://dspace.bc.uepb.edu.br/oai/requestsibuepb@setor.uepb.edu.bropendoar:2026-05-06T11:50:22Repositório Institucional da Universidade Estadual da Paraíba (UEPB) - Universidade Estadual da Paraíba (UEPB)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
dc.title.none.fl_str_mv Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
dc.title.alternative.eng.fl_str_mv Assessment of health services and quality of life for diabetics during the Covid-19 pandemic
title Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
spellingShingle Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
Guerra, Alaine de Brito
Water Treatment
Cyanobacteria
Cyanotoxins
Activated carbon
CNPQ
Tratamento de água
Cianobactérias
Cianotoxinas
Carvão ativado
title_short Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
title_full Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
title_fullStr Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
title_full_unstemmed Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
title_sort Avaliação em escala de bancada do emprego de carvão ativado granular na remoção de microcistina-LR na potabilização de águas eutrofizadas do semiárido nordestino
author Guerra, Alaine de Brito
author_facet Guerra, Alaine de Brito
author_role author
dc.contributor.advisor-co1.fl_str_mv Libânio, Marcelo
dc.contributor.advisor-co1Lattes.fl_str_mv http://lattes.cnpq.br/5168671769851394
dc.contributor.referee1.fl_str_mv Aquino, Sérgio Francisco de
dc.contributor.referee1Lattes.fl_str_mv http://lattes.cnpq.br/8758653660694681
dc.contributor.referee2.fl_str_mv Lopes, Wilton Silva
dc.contributor.advisor1.fl_str_mv Ceballos, Beatriz Suzana Ovruski de
dc.contributor.advisor1Lattes.fl_str_mv http://lattes.cnpq.br/9321950498637802
dc.contributor.authorLattes.fl_str_mv http://lattes.cnpq.br/0065347070645012
dc.contributor.author.fl_str_mv Guerra, Alaine de Brito
contributor_str_mv Libânio, Marcelo
Aquino, Sérgio Francisco de
Lopes, Wilton Silva
Ceballos, Beatriz Suzana Ovruski de
dc.subject.eng.fl_str_mv Water Treatment
Cyanobacteria
Cyanotoxins
Activated carbon
topic Water Treatment
Cyanobacteria
Cyanotoxins
Activated carbon
CNPQ
Tratamento de água
Cianobactérias
Cianotoxinas
Carvão ativado
dc.subject.cnpq.fl_str_mv CNPQ
dc.subject.por.fl_str_mv Tratamento de água
Cianobactérias
Cianotoxinas
Carvão ativado
description Usually, conventional water purification technology with eutrophic waters (high density of cyanobacteria and dissolved toxins) does not guarantee that the water produced is within the maximum allowable concentration of 1.0 µg/L of microcystin (Decree 2914/2011). Additional processes are needed, and the use of activated carbon is considered effective to reduced or eliminate those toxins. The present study aimed to evaluate in a bench-scale the removal of microcystin-LR in water supplies using conventional treatment followed by adsorption with granular activated carbon. The experiment was conducted in two stages. In the first stage coagulation assays were performed with the evaluation of five coagulants (with and without the use of polymers as auxiliaries) in order to select the most appropriate coagulant and its concentration to the water under investigation. The second stage were coagulation / flocculation tests and sedimentation using the conditions defined in the first step with raw water with an addition of a defined concentration of microcystin-LR extract. The extracted was obtained from the culture of a toxigenic strain of Microcystis aeruginosa. The final effluent was decanted in the jar test and stored. Two peristaltic pumps adduced the reserved water to the sand filters; the sand filter effluent was distributed to two columns of granular activated carbon with different particle size (0.42 to 1.40 and 0.60 to 2.36 mm). The results of coagulation assays showed the best results of removal of apparent color, turbidity, phytoplankton and particular true color, which is a strong competitor for the adsorption sites of activated carbon, with the polyaluminum chloride (dosage of 9.92 mg L -1 of Al 3 + and pH between 5 and 6, without the addition of alkalizing or acidifying). The conventional treatment steps were not efficient for microcystin-LR removal while the granular activated carbon from coconut showed high percentages of removal (80 to 100%). Although no statistically significant differences were observed in the removal of MC-LR between the different particle size, the had breakthrough coal to the smaller particle size (CC2) occurred in a shorter contact time (2 hours) which eventually reflected in a lower qe (2.1 µg/g) and a higher rate of use (8.09 gCAG / Lwater) when compared to the smaller particle size (CC1) that showed the best performance both in terms of qe (8.9 µg/g) as the rate use of (1.93 gCAG / Lwater) confirming its use in actual scale, since it ensures an effluent concentration below the Decree 2914/11 for a longer time and using a smaller quantity of coal.
publishDate 2012
dc.date.available.fl_str_mv 2012-11-30
dc.date.issued.fl_str_mv 2012-05-30
dc.date.accessioned.fl_str_mv 2015-09-25T12:19:59Z
2026-02-25T12:48:41Z
dc.type.status.fl_str_mv info:eu-repo/semantics/publishedVersion
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dc.identifier.citation.fl_str_mv GUERRA, Alaine de Brito. . 2012. 98 f. Dissertação (Mestrado em Tecnologia Ambiental) - Universidade Estadual da Paraíba, Campina Grande, 2012.
dc.identifier.uri.fl_str_mv https://repositorio.uepb.edu.br/handle/123456789/72194
dc.identifier.capesdegreeprogramcode.none.fl_str_mv 24004014005P9
identifier_str_mv GUERRA, Alaine de Brito. . 2012. 98 f. Dissertação (Mestrado em Tecnologia Ambiental) - Universidade Estadual da Paraíba, Campina Grande, 2012.
24004014005P9
url https://repositorio.uepb.edu.br/handle/123456789/72194
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Pró-Reitoria de Pós-Graduação e Pesquisa - PRPGP
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