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 | Acesso ao texto completo restrito à biblioteca da Embrapa Suínos e Aves. Para informações adicionais entre em contato com cnpsa.biblioteca@embrapa.br. |
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Registro Completo |
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Biblioteca(s): |
Embrapa Suínos e Aves. |
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Data corrente: |
10/11/2017 |
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Data da última atualização: |
10/11/2017 |
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Tipo da produção científica: |
Capítulo em Livro Técnico-Científico |
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Autoria: |
MICHELON, W.; PRANDINI, J. M.; MEZZARI, M. P.; SILVA, M. L. B. da. |
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Afiliação: |
WILLIAN MICHELON, UFSC; JEAN MICHEL PRANDINI, UFSC; MELISSA PAOLA MEZZARI, Rice University Houston; MARCIO LUIS BUSI DA SILVA, CNPSA. |
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Título: |
Phycoremediation of agro-industrial wastewaters. |
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Ano de publicação: |
2017 |
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Fonte/Imprenta: |
In: TSANG, Y. F. (Ed.) Photobioreactors: advancements, appplications and research. New York: Nova Science Publishers, Inc., [2017]. 414 p. (Environmental remediation technologies, regulations and safety). |
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Idioma: |
Inglês |
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Conteúdo: |
Abstract: This chapter addresses phycoremediation as an alternative tertiary treatment process for the removal of eutrophying nutrients from wastewaters whilst producing microalgae biomass as a valuable source of feedstock. Microalgae nutrient removal efficiency has been evaluated in laboratory and pilot-scale photobioreactors using either natural light or artificial light with specific wavelength for enhanced photosynthesis. Different reactor configurations can be utilized for phycoremediation, and these are discussed here. Operational control of hydraulic retention times in photobioreactors can lead to changes in QXWULHQW¶V bioavailability, thus contributing to significant changes in microalgal cellular composition. Without nutrient control processes, the intrinsic characteristics of a nutrientrich wastewater is likely to stimulate the growth of microalgae with high concentrations of carbohydrate and proteins, and low lipid content. Wastewater treatment facilities that use biodigesters to generate methane as biofuel can benefit from microalgae biomass. For instance, the microalgae biomass produced during the phycoremediation process is harvested and used as an alternative external source of carbon for microorganisms, thus supplementing biogas production. Furthermore, removal of CO2 and corrosive H2S can be accomplished by microalgae growing in closed system photobioreactors placed downstream from biodigesters. This integrated process results in faster nutrient removal rates from wastewater due to increased microalgae biomass growing at the expenses of higher levels of CO2. Therefore, the nutrient removal rate is not only enhanced, but a purified biomethane is also produced. Major concerns exist over several invasive and antibiotic resistant organisms thriving in wastewater effluents that are known to threaten human and animal health. Whereas several physicochemical treatments are commonly used as disinfectants (i.e., UV irradiation, use of strong oxidant radicals, pH increase, and selective membranes), most, if not all of these approaches, are difficult to operate and are usually economically unfeasible. Microalgae seem effective in the elimination of pathogens due to production of a wide range of antibacterial, antiviral, antifungal, enzyme inhibiting, immune stimulant, cytotoxic and anti-plasmodia substances. The use of microalgae-based wastewater treatment can also aid putative pathogen removal due to photosynthetic activity, which substantially increase oxygen levels and pH, thus leading to bacterial death. In a nutshell, this chapter concludes with a proposal description of integrating wastewater treatment with a microalgae culturing system in agricultural scenarios. MenosAbstract: This chapter addresses phycoremediation as an alternative tertiary treatment process for the removal of eutrophying nutrients from wastewaters whilst producing microalgae biomass as a valuable source of feedstock. Microalgae nutrient removal efficiency has been evaluated in laboratory and pilot-scale photobioreactors using either natural light or artificial light with specific wavelength for enhanced photosynthesis. Different reactor configurations can be utilized for phycoremediation, and these are discussed here. Operational control of hydraulic retention times in photobioreactors can lead to changes in QXWULHQW¶V bioavailability, thus contributing to significant changes in microalgal cellular composition. Without nutrient control processes, the intrinsic characteristics of a nutrientrich wastewater is likely to stimulate the growth of microalgae with high concentrations of carbohydrate and proteins, and low lipid content. Wastewater treatment facilities that use biodigesters to generate methane as biofuel can benefit from microalgae biomass. For instance, the microalgae biomass produced during the phycoremediation process is harvested and used as an alternative external source of carbon for microorganisms, thus supplementing biogas production. Furthermore, removal of CO2 and corrosive H2S can be accomplished by microalgae growing in closed system photobioreactors placed downstream from biodigesters. This integrated process results in faster nutrient removal rate... Mostrar Tudo |
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Palavras-Chave: |
Resistência bacteriana; Tratamento de águas residuais agrícolas. |
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Thesagro: |
Antibiótico; Bactéria; Biocombustível; Biogás; Microalga. |
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Categoria do assunto: |
-- |
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Marc: |
LEADER 03554naa a2200241 a 4500
001 2079498
005 2017-11-10
008 2017 bl uuuu u00u1 u #d
100 1 $aMICHELON, W.
245 $aPhycoremediation of agro-industrial wastewaters.$h[electronic resource]
260 $c2017
520 $aAbstract: This chapter addresses phycoremediation as an alternative tertiary treatment process for the removal of eutrophying nutrients from wastewaters whilst producing microalgae biomass as a valuable source of feedstock. Microalgae nutrient removal efficiency has been evaluated in laboratory and pilot-scale photobioreactors using either natural light or artificial light with specific wavelength for enhanced photosynthesis. Different reactor configurations can be utilized for phycoremediation, and these are discussed here. Operational control of hydraulic retention times in photobioreactors can lead to changes in QXWULHQW¶V bioavailability, thus contributing to significant changes in microalgal cellular composition. Without nutrient control processes, the intrinsic characteristics of a nutrientrich wastewater is likely to stimulate the growth of microalgae with high concentrations of carbohydrate and proteins, and low lipid content. Wastewater treatment facilities that use biodigesters to generate methane as biofuel can benefit from microalgae biomass. For instance, the microalgae biomass produced during the phycoremediation process is harvested and used as an alternative external source of carbon for microorganisms, thus supplementing biogas production. Furthermore, removal of CO2 and corrosive H2S can be accomplished by microalgae growing in closed system photobioreactors placed downstream from biodigesters. This integrated process results in faster nutrient removal rates from wastewater due to increased microalgae biomass growing at the expenses of higher levels of CO2. Therefore, the nutrient removal rate is not only enhanced, but a purified biomethane is also produced. Major concerns exist over several invasive and antibiotic resistant organisms thriving in wastewater effluents that are known to threaten human and animal health. Whereas several physicochemical treatments are commonly used as disinfectants (i.e., UV irradiation, use of strong oxidant radicals, pH increase, and selective membranes), most, if not all of these approaches, are difficult to operate and are usually economically unfeasible. Microalgae seem effective in the elimination of pathogens due to production of a wide range of antibacterial, antiviral, antifungal, enzyme inhibiting, immune stimulant, cytotoxic and anti-plasmodia substances. The use of microalgae-based wastewater treatment can also aid putative pathogen removal due to photosynthetic activity, which substantially increase oxygen levels and pH, thus leading to bacterial death. In a nutshell, this chapter concludes with a proposal description of integrating wastewater treatment with a microalgae culturing system in agricultural scenarios.
650 $aAntibiótico
650 $aBactéria
650 $aBiocombustível
650 $aBiogás
650 $aMicroalga
653 $aResistência bacteriana
653 $aTratamento de águas residuais agrícolas
700 1 $aPRANDINI, J. M.
700 1 $aMEZZARI, M. P.
700 1 $aSILVA, M. L. B. da
773 $tIn: TSANG, Y. F. (Ed.) Photobioreactors: advancements, appplications and research. New York: Nova Science Publishers, Inc., [2017]. 414 p. (Environmental remediation technologies, regulations and safety).
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Registro original: |
Embrapa Suínos e Aves (CNPSA) |
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Biblioteca |
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| Registros recuperados : 22 | |
| 4. |  | LEHN, C. R.; SALIS, S. M. de; MATTOS, P. P. de; DAMASCENO JÚNIOR, G. A. Estrutura e distribuição espacial de Trichilia Elegans A. Juss. (Meliaceae) em uma floresta semidecídua no Pantanal da Nhecolândia, Mato Grosso do Sul, Brasil. Revista de Biologia Neotropical, v. 5, n. 2, p. 1- 9, 2008.| Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 4 |
| Biblioteca(s): Embrapa Florestas; Embrapa Pantanal. |
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| 7. | | DAMASCENO JUNIOR, G. A.; POTT, A.; POTT, V. J.; SILVA, J. dos S. V. da. Florestas estacionais no Pantanal, considerações florísticas e subsídios para conservação. In: SIMPÓSIO DE GEOTECNOLOGIAS NO PANTANAL, 2., 2009, Corumbá, MS. Anais... Campinas: Embrapa Informática Agropecuária; São José dos Campos: INPE, 2009. p. 784-795. GeoPantanal 2009. Publicado também em: Geografia, Rio Claro, v. 34, p. 697-707, dez. 2009.| Tipo: Artigo em Anais de Congresso / Nota Técnica |
| Biblioteca(s): Embrapa Agricultura Digital. |
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| 9. | | SILVA, P. C. da; DAMASCENO JUNIOR, G. A.; SIMAO-BIANCHINI, R.; POTT, V. J. O genero Ipomoea L. (Convolvulaceae) na bacia da baia Negra e adjacencias, Pantanal, Ladario e Corumba. In: CONGRESSO NACIONAL DE BOTANICA, 51., 2000, Brasilia. Resumos... Brasilia: Sociedade Botanica do Brasil, 2000. p.273.| Biblioteca(s): Embrapa Pantanal. |
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| 14. | | ALVES, F. M.; LEHN, C. R.; DAMASCENO JÚNIOR, G. A.; SARTORI, A. L. B.; POTT, A.; POTT, V. J.; BORTOLOTTO, I. M.; ISHII, I. H.; SALIS, S. M. de; URBANETZ, C.; BUENO, M. L.; SCIAMARELLI, A. Coleções Botânicas do estado de Mato Grosso do Sul: situação atual e perspectivas. Iheringia, Série Botânica, Porto Alegre, n. 73, supl., p. 93-100, mar. 2018.| Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 1 |
| Biblioteca(s): Embrapa Pantanal. |
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| 15. | | CUNHA, C. N. da; BERGIER, I.; TOMAS, W. M.; DAMASCENO-JÚNIOR, G. A.; SANTOS, S. A.; ASSUNÇÃO, V. A.; SARTORI, A. L. B.; POTT, A.; ARRUDA, E. C. de; GARCIA, A. da S.; JUNK, W. J. Classificação dos macrohabitat do Pantanal Brasileiro: atualização para políticas públicas e manejo de áreas protegidas. Biodiversidade Brasileira, v. 13, n. 1, p. 1-26, 2023.| Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 4 |
| Biblioteca(s): Embrapa Pantanal. |
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| 16. | | CUNHA, C. N. da; BERGIER, I.; TOMAS, W. M.; DAMASCENO-JUNIOR, G. A.; SANTOS, S. A.; ASSUNÇÃO, V. A.; SARTORI, A. L. B.; POTT, A.; ARRUDA, E. C. de; GARCIA, A. da S.; NICOLA, R. D.; JUNK, W. J. Hydrology and vegetation base for classification of macrohabitats of the brazilian Pantanal for policy-making and management. In: DAMASCENO-JUNIOR, G. A.; POTT, A. (Ed.). Flora and Vegetation of the Pantanal Wetland. Springer Nature Switzerland AG: Cham, 2021. (Plant and Vegetation, 18). p. 365-391. Cap. 7.| Tipo: Capítulo em Livro Técnico-Científico |
| Biblioteca(s): Embrapa Pantanal. |
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| 17. | | GARCIA, L. C.; SZABO, J. K.; ROQUE, F. de O.; PEREIRA, A. de M. M.; CUNHA, C. N. da; DAMASCENO JÚNIOR, G. A.; MORATO, R. G.; TOMAS, W. M.; LIBONATI, R.; RIBEIRO, D. B. Record-breaking wildfires in the world's largest continuous tropical wetland: Integrative fire management is urgently needed for both biodiversity and humans. Journal of Environmental Management, v. 293, 112870, 2021.| Tipo: Artigo em Periódico Indexado | Circulação/Nível: A - 1 |
| Biblioteca(s): Embrapa Pantanal. |
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| 18. | | DAMASCENO JUNIOR, G. A.; ROQUE, F. de O.; GARCIA, L. C.; RIBEIRO, D. B.; TOMAS, W. M.; DIAS, E. S.; DIAS, F. A.; LIBONATI, R.; RODRIGUES, J. A.; SANTOS, F. L. M.; PEREIRA, A. de M. M.; SOUZA, E. B. de; REIS, L. K.; OLIVEIRA, M. da R.; SOUZA, A. H. de A.; PINEDA, D. A. M.; FERREIRA, B. H. dos S.; BORTOLOTTO, I. M.; POTT, A. Lessons to be learned from the wildfire catastrophe of 2020 in the Pantanal wetland. Wetland Science & Practice, v. 38, n. 2, p. 107-115, april 2021.| Tipo: Artigo em Periódico Indexado |
| Biblioteca(s): Embrapa Pantanal. |
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| 19. | | LOURIVAL, R. F. F.; SILVA, C. J. da; CALHEIROS, D. F.; ALBUQUERQUE, L. B.; BEZERRA, M. A. O.; BOOCK, A.; BORGES, L. M. R.; BOULHOSA, R. L. P.; CAMPOS, Z. M.; CATELLA, A. C.; DAMASCENO JUNIOR, G. A.; HARDOIM, E. L.; HAMILTON, S. K.; MACHADO, F. de A.; MOURAO, G. de M.; NASCIMENTO, F. L.; NOGUEIRA, F. M. B.; OLIVEIRA, M. D.; POTT, A.; SILVA, M. C.; SILVA, V. P.; TOMAS, W. Os impactos da hidrovia Paraguai-Parana sobre a biodiversidade do Pantanal - uma discussao multidisciplinar. In: SIMPOSIO SOBRE RECURSOS NATURAIS E SOCIO-ECONOMICOS DO PANTANAL, 2., 1996, Corumba, MS. Manejo e conservacao - anais. Corumba: Embrapa Pantanal, 1999. p.517-535.| Biblioteca(s): Embrapa Pantanal. |
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| 20. | | TOMAS, W. M.; ANDRADE, M. H.; BERLINCK, C. N.; BOLZAN, F.; CAMILO, A. R.; CATELLA, A. C.; CHIARAVALLOTI, R. M.; CUNHA, C. N. da; DAMASCENO JUNIOR, G. A.; FERNANDO, A. M. E.; GARCIA, L. C.; GIRARD, P.; IKEDA‐CASTRILLON, S. K.; SILVA, C. J. da; LAPS, R.; MATEUS, L.; MORATO, R. G.; MOURAO, G.; NUNES, A. V.; OLIVEIRA, M. da R.; OLIVEIRA, M. D. de; PADOVANI, C. R.; PENHA, J.; PERILLI, M. L. L.; RIBEIRO, D. B.; ROQUE, F. de O.; SORIANO, B. M. A.; STRUSSMANN, C.; TOFFOLI, C.; TORTATO, F. R.; URBANETZ, C. Eight basic principles for the elaboration of public policies and development projects for the Pantanal. Conservation Science and Practice, e13207, 2024. Online first.| Tipo: Artigo em Periódico Indexado | Circulação/Nível: B - 1 |
| Biblioteca(s): Embrapa Pantanal. |
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| Registros recuperados : 22 | |
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| Nenhum registro encontrado para a expressão de busca informada. |
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