Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier

Detalhes bibliográficos
Ano de defesa: 2024
Autor(a) principal: Popin, Gustavo Vicentini
Orientador(a): Não Informado pela instituição
Banca de defesa: Não Informado pela instituição
Tipo de documento: Tese
Tipo de acesso: Acesso aberto
Idioma: eng
Instituição de defesa: Biblioteca Digitais de Teses e Dissertações da USP
Programa de Pós-Graduação: Não Informado pela instituição
Departamento: Não Informado pela instituição
País: Não Informado pela instituição
Palavras-chave em Português:
Link de acesso: https://www.teses.usp.br/teses/disponiveis/11/11140/tde-11032025-142410/
Resumo: Land-use conversion and agricultural intensification drive widespread and rapid change of carbon (C) and nitrogen (N) on the low-relief, deep, and highly weathered soils of Amazon-Cerrado transition region of Brazil. Native vegetation removal for pasture or cropland typically leads to declines of C and N stocks in surface soils. However, less is known about the dynamic of C and N changes in deep-soil profiles. To understand the C and N dynamics in deep-soils subject to land-use change and agricultural intensification, soil samples up to 800 cm were collected beneath native forest, minimum tillage soybean, soybean-corn cropland, pasture, and a recently deforested area at Fazenda Tanguro (northeastern region of the Mato Grosso State, Brazil). In these samples, we determined soil C and N concentrations, mineral-associated organic matter (MAOM), particulate organic matter (POM), δ13C, water-extractable C (WEC) and N (WEN), ammonium (NH4+), nitrate (NO3-) and soil pH (CaCl2). The 16s rRNA and ITS amplicon sequencing was used to assess the abundance, structure, composition, and diversity of soil bacteria and fungi. Soil C stocks to 800 cm ranged from 168 Mg ha-1 to 288 Mg ha-1. Regardless the land-use, top 100 cm contained between 30% to 40% of the C stock to 800 cm, and about 50% of all soil C stocks was concentrated until 300 cm. Conversion of native forest to no-till single-cropping soybean negatively impacted soil C until 100 cm through reduction of MAOM stocks. Production intensification on the cropland led to superficial soil C accrual. Pasture showed great potential to store C through POM inputs on subsoil. The recent deforested area showed reduces in soil N stocks by 40% in the first 10 cm soil layer, but greater soil N stocks by the 100 to 300 cm soil layer compared to native forest. In cropland, N in the POM were similar to native forest, while the N linked to MAOM remained lower. Soil N stocks to 800 cm varied from 14 Mg ha-1 to 18 Mg ha-1 with no significative difference among land-uses. Overall, 40% and 60% of the total soil N stock to 800 cm were in the first 100 cm and 300 cm, respectively. Recent deforested area showed the largest soil inorganic-N (NH4+ and NO3-) stocks until 800 cm, large portion in the first 0-200 cm; cropland (both single and double crop) had the greatest inorganic-N from 200 to 600 cm. Native vegetation and double-cropped systems exhibited the highest microbial abundance, while deforested and no-till systems showed lower levels. Sequencing analysis revealed significant differences in microbial community composition, although diversity indices did not indicate substantial variation among land-uses. Furthermore, network analyses highlighted structural differences in bacterial and fungal communities influenced by land management practices. This study enhances the understanding of carbon and nitrogen dynamics in both surface and deep soils, offering valuable insights into the impacts of land-use change and agricultural intensification on soil health. Finally, based on these findings, we recommend that studies related to the impacts of agricultural expansion and intensification on the dynamics of soil C and N pools should focus efforts on sampling at least 100 cm deep in the soil, with stratified collections each 10 cm in the surface layers (up to 50 cm), and extend it to at least 300 cm, considering more areas, soil types, soil attributes, and land-uses.
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spelling Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontierMudança no uso da terra e intensificação agrícola: impactos na distribuição de carbono e nitrogênio em solos na fronteira Amazônia-CerradoAgricultura tropicalCarbon sequestrationDeep soilDeforestationDesmatamentoInorganic nitrogenMatéria orgânica do soloNitrogênio inorgânicoSequestro de carbonoSoil organic matterSolos profundosTropical agricultureLand-use conversion and agricultural intensification drive widespread and rapid change of carbon (C) and nitrogen (N) on the low-relief, deep, and highly weathered soils of Amazon-Cerrado transition region of Brazil. Native vegetation removal for pasture or cropland typically leads to declines of C and N stocks in surface soils. However, less is known about the dynamic of C and N changes in deep-soil profiles. To understand the C and N dynamics in deep-soils subject to land-use change and agricultural intensification, soil samples up to 800 cm were collected beneath native forest, minimum tillage soybean, soybean-corn cropland, pasture, and a recently deforested area at Fazenda Tanguro (northeastern region of the Mato Grosso State, Brazil). In these samples, we determined soil C and N concentrations, mineral-associated organic matter (MAOM), particulate organic matter (POM), δ13C, water-extractable C (WEC) and N (WEN), ammonium (NH4+), nitrate (NO3-) and soil pH (CaCl2). The 16s rRNA and ITS amplicon sequencing was used to assess the abundance, structure, composition, and diversity of soil bacteria and fungi. Soil C stocks to 800 cm ranged from 168 Mg ha-1 to 288 Mg ha-1. Regardless the land-use, top 100 cm contained between 30% to 40% of the C stock to 800 cm, and about 50% of all soil C stocks was concentrated until 300 cm. Conversion of native forest to no-till single-cropping soybean negatively impacted soil C until 100 cm through reduction of MAOM stocks. Production intensification on the cropland led to superficial soil C accrual. Pasture showed great potential to store C through POM inputs on subsoil. The recent deforested area showed reduces in soil N stocks by 40% in the first 10 cm soil layer, but greater soil N stocks by the 100 to 300 cm soil layer compared to native forest. In cropland, N in the POM were similar to native forest, while the N linked to MAOM remained lower. Soil N stocks to 800 cm varied from 14 Mg ha-1 to 18 Mg ha-1 with no significative difference among land-uses. Overall, 40% and 60% of the total soil N stock to 800 cm were in the first 100 cm and 300 cm, respectively. Recent deforested area showed the largest soil inorganic-N (NH4+ and NO3-) stocks until 800 cm, large portion in the first 0-200 cm; cropland (both single and double crop) had the greatest inorganic-N from 200 to 600 cm. Native vegetation and double-cropped systems exhibited the highest microbial abundance, while deforested and no-till systems showed lower levels. Sequencing analysis revealed significant differences in microbial community composition, although diversity indices did not indicate substantial variation among land-uses. Furthermore, network analyses highlighted structural differences in bacterial and fungal communities influenced by land management practices. This study enhances the understanding of carbon and nitrogen dynamics in both surface and deep soils, offering valuable insights into the impacts of land-use change and agricultural intensification on soil health. Finally, based on these findings, we recommend that studies related to the impacts of agricultural expansion and intensification on the dynamics of soil C and N pools should focus efforts on sampling at least 100 cm deep in the soil, with stratified collections each 10 cm in the surface layers (up to 50 cm), and extend it to at least 300 cm, considering more areas, soil types, soil attributes, and land-uses.A conversão do uso da terra e a intensificação agrícola impulsionam mudanças rápidas e generalizadas de carbono (C) e nitrogênio (N) dos solos da região de transição Amazônia-Cerrado no Brasil. A remoção da vegetação nativa para implementação de pastagens ou áreas de cultivo geralmente leva a diminuição dos estoques de C e N na superfície do solo. No entanto, ainda pouco se sabe sobre a dinâmica do C e N em profundidade. Para melhor entender essa dinâmica, amostras de solo até 800 cm foram coletadas sob floresta nativa, cultivo de soja com plantio mínimo, cultivo de soja-milho, pastagem e uma área recentemente desmatada na Fazenda Tanguro (região nordeste do Estado do Mato Grosso, Brasil). Nessas amostras, determinamos as concentrações de C e N do solo, estoques de matéria orgânica associada a minerais (MAOM), matéria orgânica particulada (POM), δ13C, C extraível em água (WEC) e N (WEN), amônio (NH4+), nitrato (NO3-) e pH do solo (CaCl2). O sequenciação dos genes 16s rRNA e ITS foi usado para avaliar a abundância, estrutura, composição e diversidade de bactérias e fungos do solo. Os estoques totais de C do solo até 800 cm variaram entre 168 Mg ha-1 a 288 Mg ha-1. Independentemente do uso da terra, os 100 cm superiores continham entre 30% e 40% do estoque de C até 800 cm, e cerca de 50% de todos os estoques de C do solo estavam concentrados até 300 cm. A conversão da floresta nativa para o cultivo de soja em plantio direto impactou negativamente o C do solo até 100 cm através da redução dos estoques de MAOM. A intensificação da produção no cultivo resultou em acúmulo de C no solo superficial. A pastagem mostrou grande potencial para armazenar C através da entrada de POM no subsolo. A área recentemente desmatada mostrou reduções nos estoques de N do solo em 40% na camada 0-10 cm, mas maiores estoques de N na camada de 100 a 300 cm em comparação com a floresta nativa. Nas áreas de cultivo, o N associado a POM foi semelhante à floresta nativa, enquanto o N ligado ao MAOM foi menor. Os estoques de N do solo até 800 cm variaram de 14 Mg ha-1 a 18 Mg ha-1, sem diferença significativa entre os usos da terra. No geral, 40% e 60% do estoque total de N do solo até 800 cm estavam nos primeiros 100 cm e 300 cm, respectivamente. A área recentemente desmatada apresentou os maiores estoques de N inorgânico do solo (NH44 + e NO34 -) até 800 cm, com grande parcela desse montante nos primeiros 0-200 cm; o cultivo (tanto monocultivo quanto cultivo duplo) teve o maior N inorgânico de 200 a 600 cm. A vegetação nativa e o sistema de cultivo duplo exibiram a maior abundância microbiana, enquanto a área desmatada e de cultivo de soja mostraram níveis mais baixos. O sequenciamento revelou diferenças significativas na composição das comunidades microbianas, embora os índices de diversidade não indicaram variação substancial entre os usos da terra. Além disso, as análises de rede destacaram diferenças estruturais nas comunidades bacterianas e fúngicas influenciadas pelas práticas de manejo da terra. Este estudo aprimora a compreensão das dinâmicas de carbono e nitrogênio tanto na superfície quanto em profundidade, oferecendo informações valiosas sobre os impactos da mudança de uso da terra e da intensificação agrícola na saúde do solo. Finalmente, com base nessas descobertas, recomendamos que estudos relacionados aos impactos da expansão e intensificação agrícola nas dinâmicas dos estoques de C e N do solo concentrem esforços na amostragem de pelo menos 100 cm de profundidade no solo, com coletas estratificadas a cada 10 cm nas camadas superficiais (até 50 cm), e se estendam para pelo menos 300 cm, considerando mais áreas, tipos de solo, atributos do solo e usos da terra.Biblioteca Digitais de Teses e Dissertações da USPCerri, Carlos Eduardo PellegrinoPopin, Gustavo Vicentini2024-12-02info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/doctoralThesisapplication/pdfhttps://www.teses.usp.br/teses/disponiveis/11/11140/tde-11032025-142410/reponame:Biblioteca Digital de Teses e Dissertações da USPinstname:Universidade de São Paulo (USP)instacron:USPReter o conteúdo por motivos de patente, publicação e/ou direitos autoriais.info:eu-repo/semantics/openAccesseng2025-03-18T14:44:02Zoai:teses.usp.br:tde-11032025-142410Biblioteca Digital de Teses e Dissertaçõeshttp://www.teses.usp.br/PUBhttp://www.teses.usp.br/cgi-bin/mtd2br.plvirginia@if.usp.br|| atendimento@aguia.usp.br||virginia@if.usp.bropendoar:27212025-03-18T14:44:02Biblioteca Digital de Teses e Dissertações da USP - Universidade de São Paulo (USP)false
dc.title.none.fl_str_mv Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
Mudança no uso da terra e intensificação agrícola: impactos na distribuição de carbono e nitrogênio em solos na fronteira Amazônia-Cerrado
title Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
spellingShingle Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
Popin, Gustavo Vicentini
Agricultura tropical
Carbon sequestration
Deep soil
Deforestation
Desmatamento
Inorganic nitrogen
Matéria orgânica do solo
Nitrogênio inorgânico
Sequestro de carbono
Soil organic matter
Solos profundos
Tropical agriculture
title_short Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
title_full Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
title_fullStr Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
title_full_unstemmed Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
title_sort Land-use change and agricultural intensification: impacts on carbon and nitrogen distribution in soil profiles of the Amazon-Cerrado frontier
author Popin, Gustavo Vicentini
author_facet Popin, Gustavo Vicentini
author_role author
dc.contributor.none.fl_str_mv Cerri, Carlos Eduardo Pellegrino
dc.contributor.author.fl_str_mv Popin, Gustavo Vicentini
dc.subject.por.fl_str_mv Agricultura tropical
Carbon sequestration
Deep soil
Deforestation
Desmatamento
Inorganic nitrogen
Matéria orgânica do solo
Nitrogênio inorgânico
Sequestro de carbono
Soil organic matter
Solos profundos
Tropical agriculture
topic Agricultura tropical
Carbon sequestration
Deep soil
Deforestation
Desmatamento
Inorganic nitrogen
Matéria orgânica do solo
Nitrogênio inorgânico
Sequestro de carbono
Soil organic matter
Solos profundos
Tropical agriculture
description Land-use conversion and agricultural intensification drive widespread and rapid change of carbon (C) and nitrogen (N) on the low-relief, deep, and highly weathered soils of Amazon-Cerrado transition region of Brazil. Native vegetation removal for pasture or cropland typically leads to declines of C and N stocks in surface soils. However, less is known about the dynamic of C and N changes in deep-soil profiles. To understand the C and N dynamics in deep-soils subject to land-use change and agricultural intensification, soil samples up to 800 cm were collected beneath native forest, minimum tillage soybean, soybean-corn cropland, pasture, and a recently deforested area at Fazenda Tanguro (northeastern region of the Mato Grosso State, Brazil). In these samples, we determined soil C and N concentrations, mineral-associated organic matter (MAOM), particulate organic matter (POM), δ13C, water-extractable C (WEC) and N (WEN), ammonium (NH4+), nitrate (NO3-) and soil pH (CaCl2). The 16s rRNA and ITS amplicon sequencing was used to assess the abundance, structure, composition, and diversity of soil bacteria and fungi. Soil C stocks to 800 cm ranged from 168 Mg ha-1 to 288 Mg ha-1. Regardless the land-use, top 100 cm contained between 30% to 40% of the C stock to 800 cm, and about 50% of all soil C stocks was concentrated until 300 cm. Conversion of native forest to no-till single-cropping soybean negatively impacted soil C until 100 cm through reduction of MAOM stocks. Production intensification on the cropland led to superficial soil C accrual. Pasture showed great potential to store C through POM inputs on subsoil. The recent deforested area showed reduces in soil N stocks by 40% in the first 10 cm soil layer, but greater soil N stocks by the 100 to 300 cm soil layer compared to native forest. In cropland, N in the POM were similar to native forest, while the N linked to MAOM remained lower. Soil N stocks to 800 cm varied from 14 Mg ha-1 to 18 Mg ha-1 with no significative difference among land-uses. Overall, 40% and 60% of the total soil N stock to 800 cm were in the first 100 cm and 300 cm, respectively. Recent deforested area showed the largest soil inorganic-N (NH4+ and NO3-) stocks until 800 cm, large portion in the first 0-200 cm; cropland (both single and double crop) had the greatest inorganic-N from 200 to 600 cm. Native vegetation and double-cropped systems exhibited the highest microbial abundance, while deforested and no-till systems showed lower levels. Sequencing analysis revealed significant differences in microbial community composition, although diversity indices did not indicate substantial variation among land-uses. Furthermore, network analyses highlighted structural differences in bacterial and fungal communities influenced by land management practices. This study enhances the understanding of carbon and nitrogen dynamics in both surface and deep soils, offering valuable insights into the impacts of land-use change and agricultural intensification on soil health. Finally, based on these findings, we recommend that studies related to the impacts of agricultural expansion and intensification on the dynamics of soil C and N pools should focus efforts on sampling at least 100 cm deep in the soil, with stratified collections each 10 cm in the surface layers (up to 50 cm), and extend it to at least 300 cm, considering more areas, soil types, soil attributes, and land-uses.
publishDate 2024
dc.date.none.fl_str_mv 2024-12-02
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