Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem

Detalhes bibliográficos
Ano de defesa: 2021
Autor(a) principal: Souza, Camila da Costa Barros de lattes
Orientador(a): Amaral Sobrinho, Nelson Moura Brasil do lattes
Banca de defesa: Amaral Sobrinho, Nelson Moura Brasil do lattes, Lima, Erica Souto Abreu lattes, Pinheiro, ?rika Fl?via Machado lattes, Leal, Marco Antonio de Almeida lattes, Parente, Cl?udio Ernesto Taveira lattes
Tipo de documento: Tese
Tipo de acesso: Acesso aberto
Idioma: por
Instituição de defesa: Universidade Federal Rural do Rio de Janeiro
Programa de Pós-Graduação: Programa de P?s-Gradua??o em Agronomia - Ci?ncia do Solo
Departamento: Instituto de Agronomia
País: Brasil
Palavras-chave em Português:
Adubo org?nico
Avicultura
Subst?ncias h?micas
Eruca sativa
Palavras-chave em Inglês:
Organic fertilizer
Aviculture
Humic substances
Eruca sativa
Área do conhecimento CNPq:
Agronomia
Link de acesso: https://tede.ufrrj.br/jspui/handle/jspui/6428
Resumo: The presence of contaminants in poultry litter (PL), such as heavy metals, makes its use in agriculture a major challenge. This work aimed to evaluate the chemical changes that occur in the structure of organic matter (OM) PL during its composting, and the evolution in the structure of humic substances (HS) formed during this process, and thus determine the relationship between the structural changes of organic matter during composting with the bioavailability of heavy metals present in PL and their transfer to plants, in addition to the ability of this residue to adsorb Pb and Cu metals. In chapter 1, a preliminary study was carried out on the role of the OM structure of PL in the changes in the solubility of heavy metals present in this residue during the initial stage of composting. In the first thirty days of composting, favoring more stable interactions between heavy metals and the most recalcitrant organic fraction of PL reduced the solubility of these elements and, consequently, the polluting potential of PL. In chapter 2, a characterization of the changes in the organic structure of PL and in the humic fractions formed during the composting process is presented through structural elucidation techniques. It was found that during composting the aliphatic and carboxylic structures are replaced by aromatic compounds in the HA, while the polarity and the presence of oxygenated functional groups increase in the FA. The evolution of humic structures in the PL during composting favored the preservation of nitrogenous structures and the high presence of carbohydrates in this residue at the end of the process. Chapter 3 presents the action of the OM of PL, and its transformations during the entire composting process, on the bioavailability of heavy metals in the environment. The most recalcitrant chemical forms of heavy metals increased during composting due to the affinity of these elements with the oxidized structures of SH formed during the composting process. However, the association of Pb with the oxygenated aliphatic carbon structures of the SH formed during composting contributed to the increase of its water-soluble fraction. Chapter 4 describes the adsorption phenomena of Cu and Pb in PL compounds with different composting times. The linear model proved to be more adequate to describe the process of adsorption of Cu and Pb, in all evaluated composting times. The non-composted PL showed a higher adsorption by Pb, while the composted PL showed a higher adsorption by Cu. However, regardless of the composting time, the adsorption of Cu and Pb in PL occurred predominantly in a specific way. In chapter 5, the transfer of heavy metals to the arugula plant (Eruca sativa) is presented when it is fertilized with PL in different stages of composting. The application of PL, regardless of the composting time, reduced the Mn contents and increased the Cu contents in the plant. The greater affinity of Pb for highly lable structures contributed to its increase in arugula. The increase in the water-soluble and exchangeable fractions of Zn in the soil resulting from the application of PL also favored the increase of Zn contents in the arugula. Thus, the increase in structures of high lability of oxygenated aliphatic carbons in the HS with the composting time, reflecting in the final characteristics of the compound, may be favoring the non-specific adsorption of Pb, increasing the participation of this metal in the water-soluble fraction and contributing to the absorption of this by the arugula plant
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spelling Amaral Sobrinho, Nelson Moura Brasil do509.422.127-20https://orcid.org/0000-0002-5053-7338http://lattes.cnpq.br/8349031396398015Garc?a, Andr?s Calder?nhttps://orcid.org/0000-0001-5963-3847http://lattes.cnpq.br/8896375232574274Amaral Sobrinho, Nelson Moura Brasil do509.422.127-20https://orcid.org/0000-0002-5053-7338http://lattes.cnpq.br/8349031396398015Lima, Erica Souto Abreuhttps://orcid.org/0000-0003-4140-3634http://lattes.cnpq.br/6111184982796209Pinheiro, ?rika Fl?via Machadohttps://orcid.org/0000-0001-9039-4127http://lattes.cnpq.br/8101589624388403Leal, Marco Antonio de Almeidahttps://orcid.org/0000-0003-3988-2277http://lattes.cnpq.br/6687333214208685Parente, Cl?udio Ernesto Taveirahttps://orcid.org/0000-0002-8904-3968http://lattes.cnpq.br/5733011042168647120.208.257-24https://orcid.org/0000-0002-5253-3197http://lattes.cnpq.br/3672142883162627Souza, Camila da Costa Barros de2023-03-17T14:37:13Z2021-09-13SOUZA, Camila da Costa Barros de. Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem. 2021.162 f. Tese (Doutorado em Agronomia - Ci?ncia do Solo) - Instituto de Agronomia, Universidade Federal Rural do Rio de Janeiro, Serop?dica, 2021.https://tede.ufrrj.br/jspui/handle/jspui/6428The presence of contaminants in poultry litter (PL), such as heavy metals, makes its use in agriculture a major challenge. This work aimed to evaluate the chemical changes that occur in the structure of organic matter (OM) PL during its composting, and the evolution in the structure of humic substances (HS) formed during this process, and thus determine the relationship between the structural changes of organic matter during composting with the bioavailability of heavy metals present in PL and their transfer to plants, in addition to the ability of this residue to adsorb Pb and Cu metals. In chapter 1, a preliminary study was carried out on the role of the OM structure of PL in the changes in the solubility of heavy metals present in this residue during the initial stage of composting. In the first thirty days of composting, favoring more stable interactions between heavy metals and the most recalcitrant organic fraction of PL reduced the solubility of these elements and, consequently, the polluting potential of PL. In chapter 2, a characterization of the changes in the organic structure of PL and in the humic fractions formed during the composting process is presented through structural elucidation techniques. It was found that during composting the aliphatic and carboxylic structures are replaced by aromatic compounds in the HA, while the polarity and the presence of oxygenated functional groups increase in the FA. The evolution of humic structures in the PL during composting favored the preservation of nitrogenous structures and the high presence of carbohydrates in this residue at the end of the process. Chapter 3 presents the action of the OM of PL, and its transformations during the entire composting process, on the bioavailability of heavy metals in the environment. The most recalcitrant chemical forms of heavy metals increased during composting due to the affinity of these elements with the oxidized structures of SH formed during the composting process. However, the association of Pb with the oxygenated aliphatic carbon structures of the SH formed during composting contributed to the increase of its water-soluble fraction. Chapter 4 describes the adsorption phenomena of Cu and Pb in PL compounds with different composting times. The linear model proved to be more adequate to describe the process of adsorption of Cu and Pb, in all evaluated composting times. The non-composted PL showed a higher adsorption by Pb, while the composted PL showed a higher adsorption by Cu. However, regardless of the composting time, the adsorption of Cu and Pb in PL occurred predominantly in a specific way. In chapter 5, the transfer of heavy metals to the arugula plant (Eruca sativa) is presented when it is fertilized with PL in different stages of composting. The application of PL, regardless of the composting time, reduced the Mn contents and increased the Cu contents in the plant. The greater affinity of Pb for highly lable structures contributed to its increase in arugula. The increase in the water-soluble and exchangeable fractions of Zn in the soil resulting from the application of PL also favored the increase of Zn contents in the arugula. Thus, the increase in structures of high lability of oxygenated aliphatic carbons in the HS with the composting time, reflecting in the final characteristics of the compound, may be favoring the non-specific adsorption of Pb, increasing the participation of this metal in the water-soluble fraction and contributing to the absorption of this by the arugula plantA presen?a de contaminantes na cama de frango (CF), como os metais pesados, torna a sua utiliza??o na agricultura um grande desafio. Este trabalho teve por objetivo avaliar as altera??es qu?micas que ocorrem na estrutura da mat?ria org?nica (MO) da CF durante a sua compostagem, e a evolu??o na estrutura das subst?ncias h?micas (SH) formadas durante esse processo, e, assim, determinar a rela??o entre as altera??es estruturais da MO durante a compostagem com a biodisponibilidade dos metais pesados presentes na CF e sua transfer?ncia para as plantas, al?m da capacidade desse res?duo de adsorver os metais Pb e Cu. No cap?tulo 1, foi realizado um estudo preliminar sobre o papel da estrutura da MO da CF nas altera??es da solubilidade dos metais pesados presentes nesse res?duo durante o est?gio inicial da compostagem. Nos primeiros trinta dias de compostagem, o favorecimento de intera??es mais est?veis entre os metais pesados e a fra??o org?nica mais recalcitrante da CF reduziu a solubilidade desses elementos e, consequentemente, o potencial poluidor da CF. No cap?tulo 2, ? apresentada uma caracteriza??o das altera??es na estrutura org?nica da CF e nas fra??es h?micas formadas durante o processo de compostagem mediante t?cnicas de elucida??o estrutural. Verificou-se que durante a compostagem as estruturas alif?ticas e carbox?licas s?o substitu?das por compostos arom?ticos nos AH, enquanto que a polaridade e a presen?a de grupamentos funcionais oxigenados aumentam nos AF. A evolu??o das estruturas h?micas na CF durante a compostagem favoreceu a preserva??o de estruturas nitrogenadas e a elevada presen?a de carboidratos nesse res?duo ao final do processo. O cap?tulo 3, apresenta a a??o da MO da CF, e das suas transforma??es durante toda a compostagem, na biodisponibilidade dos metais pesados no ambiente. As formas qu?micas mais recalcitrantes dos metais pesados aumentaram durante a compostagem devido ? afinidade desses elementos com as estruturas oxidadas das SH formadas durante o processo de compostagem. Entretanto, a associa??o do Pb com as estruturas de carbono alif?ticos oxigenados das SH formadas durante a compostagem contribuiu para a o aumento da sua fra??o hidrossol?vel. O cap?tulo 4 descreve os fen?menos de adsor??o do Cu e Pb em compostos de CF com diferentes tempos de compostagem. O modelo linear mostrou-se mais adequado para descrever o processo de adsor??o do Cu e do Pb, em todos os tempos de compostagem avaliados. A CF n?o compostada apresentou uma maior adsor??o pelo Pb, enquanto que a CF compostada apresentou maior adsor??o pelo Cu. Contudo, independente do tempo de compostagem, a adsor??o do Cu e do Pb na CF ocorreu, predominantemente, de forma espec?fica. No cap?tulo 5, ? apresentado a transfer?ncia de metais pesados ? planta de r?cula (Eruca sativa) quando a mesma ? aduba com CF em diferentes est?gios de compostagem. A aplica??o da CF, independentemente do tempo de compostagem, reduziu os teores de Mn e aumentou os teores de Cu na planta. A maior afinidade do Pb por estruturas de elevada labilidade contribuiu para o seu incremento na r?cula. O aumento das fra??es hidrossol?vel e troc?vel do Zn no solo decorrente da aplica??o de CF, tamb?m favoreceu o aumento dos teores de Zn na r?cula. Assim, o incremento de estruturas de elevada labilidade de carbonos alif?ticos oxigenados nas SH com o tempo de compostagem, refletindo nas caracter?sticas finais do composto, pode estar favorecendo a adsor??o n?o espec?fica do Pb, aumentando a participa??o desse metal na fra??o hidrossol?vel e contribuindo para a absor??o desse pela planta de r?culaSubmitted by Celso Magalhaes (celsomagalhaes@ufrrj.br) on 2023-03-17T14:37:13Z No. of bitstreams: 1 2021 - Camila da Costa Barros de Souza.pdf: 4606760 bytes, checksum: c87ad7c826bb13676d5c630c0ca35090 (MD5)Made available in DSpace on 2023-03-17T14:37:13Z (GMT). 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dc.title.por.fl_str_mv Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
dc.title.alternative.eng.fl_str_mv Chemical, structural, and heavy metal adsorption changes in poultry litter during composting
title Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
spellingShingle Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
Souza, Camila da Costa Barros de
Adubo org?nico
Avicultura
Subst?ncias h?micas
Eruca sativa
Organic fertilizer
Aviculture
Humic substances
Eruca sativa
Agronomia
title_short Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
title_full Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
title_fullStr Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
title_full_unstemmed Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
title_sort Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem
author Souza, Camila da Costa Barros de
author_facet Souza, Camila da Costa Barros de
author_role author
dc.contributor.advisor1.fl_str_mv Amaral Sobrinho, Nelson Moura Brasil do
dc.contributor.advisor1ID.fl_str_mv 509.422.127-20
https://orcid.org/0000-0002-5053-7338
dc.contributor.advisor1Lattes.fl_str_mv http://lattes.cnpq.br/8349031396398015
dc.contributor.advisor-co1.fl_str_mv Garc?a, Andr?s Calder?n
dc.contributor.advisor-co1ID.fl_str_mv https://orcid.org/0000-0001-5963-3847
dc.contributor.advisor-co1Lattes.fl_str_mv http://lattes.cnpq.br/8896375232574274
dc.contributor.referee1.fl_str_mv Amaral Sobrinho, Nelson Moura Brasil do
dc.contributor.referee1ID.fl_str_mv 509.422.127-20
https://orcid.org/0000-0002-5053-7338
dc.contributor.referee1Lattes.fl_str_mv http://lattes.cnpq.br/8349031396398015
dc.contributor.referee2.fl_str_mv Lima, Erica Souto Abreu
dc.contributor.referee2ID.fl_str_mv https://orcid.org/0000-0003-4140-3634
dc.contributor.referee2Lattes.fl_str_mv http://lattes.cnpq.br/6111184982796209
dc.contributor.referee3.fl_str_mv Pinheiro, ?rika Fl?via Machado
dc.contributor.referee3ID.fl_str_mv https://orcid.org/0000-0001-9039-4127
dc.contributor.referee3Lattes.fl_str_mv http://lattes.cnpq.br/8101589624388403
dc.contributor.referee4.fl_str_mv Leal, Marco Antonio de Almeida
dc.contributor.referee4ID.fl_str_mv https://orcid.org/0000-0003-3988-2277
dc.contributor.referee4Lattes.fl_str_mv http://lattes.cnpq.br/6687333214208685
dc.contributor.referee5.fl_str_mv Parente, Cl?udio Ernesto Taveira
dc.contributor.referee5ID.fl_str_mv https://orcid.org/0000-0002-8904-3968
dc.contributor.referee5Lattes.fl_str_mv http://lattes.cnpq.br/5733011042168647
dc.contributor.authorID.fl_str_mv 120.208.257-24
https://orcid.org/0000-0002-5253-3197
dc.contributor.authorLattes.fl_str_mv http://lattes.cnpq.br/3672142883162627
dc.contributor.author.fl_str_mv Souza, Camila da Costa Barros de
contributor_str_mv Amaral Sobrinho, Nelson Moura Brasil do
Garc?a, Andr?s Calder?n
Amaral Sobrinho, Nelson Moura Brasil do
Lima, Erica Souto Abreu
Pinheiro, ?rika Fl?via Machado
Leal, Marco Antonio de Almeida
Parente, Cl?udio Ernesto Taveira
dc.subject.por.fl_str_mv Adubo org?nico
Avicultura
Subst?ncias h?micas
Eruca sativa
topic Adubo org?nico
Avicultura
Subst?ncias h?micas
Eruca sativa
Organic fertilizer
Aviculture
Humic substances
Eruca sativa
Agronomia
dc.subject.eng.fl_str_mv Organic fertilizer
Aviculture
Humic substances
Eruca sativa
dc.subject.cnpq.fl_str_mv Agronomia
description The presence of contaminants in poultry litter (PL), such as heavy metals, makes its use in agriculture a major challenge. This work aimed to evaluate the chemical changes that occur in the structure of organic matter (OM) PL during its composting, and the evolution in the structure of humic substances (HS) formed during this process, and thus determine the relationship between the structural changes of organic matter during composting with the bioavailability of heavy metals present in PL and their transfer to plants, in addition to the ability of this residue to adsorb Pb and Cu metals. In chapter 1, a preliminary study was carried out on the role of the OM structure of PL in the changes in the solubility of heavy metals present in this residue during the initial stage of composting. In the first thirty days of composting, favoring more stable interactions between heavy metals and the most recalcitrant organic fraction of PL reduced the solubility of these elements and, consequently, the polluting potential of PL. In chapter 2, a characterization of the changes in the organic structure of PL and in the humic fractions formed during the composting process is presented through structural elucidation techniques. It was found that during composting the aliphatic and carboxylic structures are replaced by aromatic compounds in the HA, while the polarity and the presence of oxygenated functional groups increase in the FA. The evolution of humic structures in the PL during composting favored the preservation of nitrogenous structures and the high presence of carbohydrates in this residue at the end of the process. Chapter 3 presents the action of the OM of PL, and its transformations during the entire composting process, on the bioavailability of heavy metals in the environment. The most recalcitrant chemical forms of heavy metals increased during composting due to the affinity of these elements with the oxidized structures of SH formed during the composting process. However, the association of Pb with the oxygenated aliphatic carbon structures of the SH formed during composting contributed to the increase of its water-soluble fraction. Chapter 4 describes the adsorption phenomena of Cu and Pb in PL compounds with different composting times. The linear model proved to be more adequate to describe the process of adsorption of Cu and Pb, in all evaluated composting times. The non-composted PL showed a higher adsorption by Pb, while the composted PL showed a higher adsorption by Cu. However, regardless of the composting time, the adsorption of Cu and Pb in PL occurred predominantly in a specific way. In chapter 5, the transfer of heavy metals to the arugula plant (Eruca sativa) is presented when it is fertilized with PL in different stages of composting. The application of PL, regardless of the composting time, reduced the Mn contents and increased the Cu contents in the plant. The greater affinity of Pb for highly lable structures contributed to its increase in arugula. The increase in the water-soluble and exchangeable fractions of Zn in the soil resulting from the application of PL also favored the increase of Zn contents in the arugula. Thus, the increase in structures of high lability of oxygenated aliphatic carbons in the HS with the composting time, reflecting in the final characteristics of the compound, may be favoring the non-specific adsorption of Pb, increasing the participation of this metal in the water-soluble fraction and contributing to the absorption of this by the arugula plant
publishDate 2021
dc.date.issued.fl_str_mv 2021-09-13
dc.date.accessioned.fl_str_mv 2023-03-17T14:37:13Z
dc.type.status.fl_str_mv info:eu-repo/semantics/publishedVersion
dc.type.driver.fl_str_mv info:eu-repo/semantics/doctoralThesis
format doctoralThesis
status_str publishedVersion
dc.identifier.citation.fl_str_mv SOUZA, Camila da Costa Barros de. Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem. 2021.162 f. Tese (Doutorado em Agronomia - Ci?ncia do Solo) - Instituto de Agronomia, Universidade Federal Rural do Rio de Janeiro, Serop?dica, 2021.
dc.identifier.uri.fl_str_mv https://tede.ufrrj.br/jspui/handle/jspui/6428
identifier_str_mv SOUZA, Camila da Costa Barros de. Altera??es qu?micas, estruturais e na capacidade de adsor??o de metais pesados da cama de frango durante a compostagem. 2021.162 f. Tese (Doutorado em Agronomia - Ci?ncia do Solo) - Instituto de Agronomia, Universidade Federal Rural do Rio de Janeiro, Serop?dica, 2021.
url https://tede.ufrrj.br/jspui/handle/jspui/6428
dc.language.iso.fl_str_mv por
language por
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