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dc.contributor.authorMonteiro, Rafael Cassador-
dc.date.accessioned2025-09-05T13:54:37Z-
dc.date.available2025-09-05T13:54:37Z-
dc.date.issued2021-12-03-
dc.identifier.citationMONTEIRO, Rafael Cassador. Efeito da introdução de Arachis pintoi cv. Belomonte em pastagens de Brachiaria brizantha cv. Marandú na produção leiteira e dinâmica de nitrogênio. 2020. 99 f. Tese (Doutorado em Agronomia, Ciência do Solo) - Instituto de Agronomia, Universidade Federal Rural do Rio de Janeiro, Seropédica, 2020.pt_BR
dc.identifier.urihttps://rima.ufrrj.br/jspui/handle/20.500.14407/23136-
dc.description.abstractAs mudanças climáticas são uma preocupação mundial. No Brasil aproximadamente um terço de todas as emissões de gases efeito estufa (GEE) de fontes antrópicas vem das atividades agropecuárias, e emissões de pastagens e bovinos dominam este setor. Neste contexto surge como alternativa as leguminosas forrageiras fixadoras de nitrogênio que aumentam a qualidade do pasto e dispensam fertilização nitrogenada. Contudo, ainda existem questionamentos acerca do impacto das leguminosas na produção animal, emissões de GEE nas excretas e a ciclagem de N no sistema solo/planta/animal. O objetivo do trabalho foi comparar o efeito da introdução do amendoim forrageiro (Arachis pintoi cv. Belomonte) em pastagens de capim Marandú (Brachiaria brizantha cv. Marandú) e um sistema fertilizado com N na produção leiteira, emissão de GEE e a ciclagem de N. O estudo foi desenvolvido na Estação Experimental da Comissão Executiva do Plano da Lavoura Cacaueira (CEPLAC) em Itabela – BA. O delineamento experimental utilizado foi blocos casualizados com 3 repetições de 2 tratamentos, capim Marandú fertilizado com 120 kg N ha-1 ano-1 (Bb+N) ou consorciado com amendoim forrageiro (Bb+Ar). Na avaliação das emissões de GEE um terceiro tratamento foi adicionado: pastagem degradada (Deg). O regime climático influenciou na produção de leite. As épocas de maior precipitação proporcionaram maior oferta de forragem com melhor qualidade nutricional que refletiu na produção de leite. A produção por ciclo de avaliação (84 dias) variou entre 255 e 658 kg leite ha-1. Em média Bb+Ar produziu 512 kg leite ha-1 enquanto Bb+N 477 kg leite ha-1. A avaliação de δ 13C das fezes mostrou que o consumo de amendoim representou 13 % da dieta dos animais. Na primeira aplicação de excretas a proporção do N das excretas (fator de emissão – FE) volatilizada como amônia (NH3) foi de 2,37% 2,43% e 3,60% e na segunda 6,80%, 1,98% e 6,22%, Deg, Bb+N e Bb+Ar respectivamente. As fezes praticamente não emitiram NH3. A volatilização do N da ureia fertilizante representou 1,97% e 2,50% na primeira e segunda aplicação, respectivamente. Na primeira aplicação os FE-urina de N2O foi de 1,36%, 3,85% e 1,41%, Deg, Bb+N e Bb+Ar, respectivamente. Nesta aplicação o FE do tratamento Bb+N foi maior dos demais. Na segunda aplicação os FE foram drasticamente reduzidos para 0,28%; 0,31% 0,19% Deg, Bb+N e Bb+Ar, respectivamente. O FE de N2O para ureia foi de 4,5% e 0,4%, primeira e segunda aplicação, respectivamente. A introdução do amendoim não alterou a taxa ‘k’ da decomposição dos resíduos vegetais (liteira) das forrageiras. Para os 6 dias do pastejo e os primeiro 6 dias de descanso, o “k” médio foi de 0,0904 g g-1 dia-1, enquanto que para os 28 dias subsequentes de descanso foi 0,0570 g g-1 dia-1. A proporção de amendoim na liteira variou entre 1 e 7%. A adição de N via FBN na liteira foi de 10,6 kg N ha-1 ano-1. A introdução de amendoim forrageiro se mostra promissor para a produção de leite. Houve um aumento das emissões de NH3 das excretas de Bb+Ar e diminuição das emissões de N2O. A FBN foi capaz de suprir a demanda de N. A intensidade das emissões dos GEE (excluindo metano entérico) caiu de 470 g CO2eq para 70 g CO2eq kg de leite-1 quando o fertilizante foi substituído pelo amendoim forrageiro.pt_BR
dc.description.sponsorshipConselho Nacional de Pesquisa e Desenvolvimento Científico e Tecnológico - CNPqpt_BR
dc.description.sponsorshipCoordenação de Aperfeiçoamento de Pessoal de Nível Superior - CAPESpt_BR
dc.description.sponsorshipFundação de Amparo à Pesquisa do Estado do Rio de Janeiro - FAPERJpt_BR
dc.languageporpt_BR
dc.publisherUniversidade Federal Rural do Rio de Janeiropt_BR
dc.subjectBrachiariapt_BR
dc.subjectGEEpt_BR
dc.subjectLeguminosaspt_BR
dc.subjectLeitept_BR
dc.subjectNitrogêniopt_BR
dc.subjectGHGspt_BR
dc.subjectForage legumept_BR
dc.subjectMilkpt_BR
dc.subjectNitrogenpt_BR
dc.titleEfeito da introdução de Arachis pintoi cv. Belomonte em pastagens de Brachiaria brizantha cv. Marandú na produção leiteira e dinâmica de nitrogêniopt_BR
dc.title.alternativeEffect of the introduction of Arachis pintoi cv. Belomonte in pastures of Brachiaria brizantha cv. Marandú on dairy production and nitrogen dynamicsen
dc.typeTesept_BR
dc.description.abstractOtherClimate change is of worldwide concern. In Brazil, approximately one third of all greenhouse gas emissions (GHGs) from anthropogenic sources come from agricultural activities, and emissions from pastures and cattle dominate this sector. In this context, nitrogen-fixing forage legumes appear as an alternative to improve the quality of the pasture and to dispense with nitrogen fertilization. However, there are still questions about the impact of legumes on animal production, emissions of GHGs in excreta and the cycling of N in the soil/plant/animal system. The objective of the study was to compare the effect of the introduction of forage peanut (Arachis pintoi cv. Belomonte) in Marandú grass pastures (Brachiaria brizantha cv. Marandú) and an N fertilized system in the context of dairy production, GHG emissions and N cycling. The study was carried out at the Experimental Station of the Executive Committee of the Cocoa Crop (CEPLAC) in Itabela - BA. The experimental design used was randomized blocks with 3 replicates of 2 treatments, Marandú grass fertilized with 120 kg N ha-1 year-1 (Bb + N) or intercropped with forage peanut (Bb + Ar). For the assessment of GHG emissions, a third treatment was added: degraded pasture (Deg). Each plot was composed of 6 paddocks, the grazing system was rotated with 6 days of occupation and 30 days of rest. The climatic regime influenced milk production. The periods of greater precipitation provided a greater supply of forage with better nutritional quality, which was reflected in milk production. The milk production for each grazing cycle (84 days) varied from 255 to 658 kg milk ha-1, yr-1. On average Bb + Ar produced 512 kg milk ha-1 while Bb + N 477 kg milk ha-1 . The δ 13C evaluation of feces showed that forage peanut consumption represented 13% of the animals' diet. In the first application of excreta the proportion of N of excreta (emission factor - FE) volatilized as ammonia (NH3) was 2.37% 2.43% and 3.60% and in the second 6.80%, 1.98 % and 6.22%, Deg, Bb + N and Bb + Ar respectively. The feces emitted practically no NH3. The volatilization of N from fertilizer urea represented 1.97% and 2.50% in the first and second application, respectively. In the first application, the N2O the FE-urine was 1.36%, 3.85% and 1.41%, Deg, Bb + N and Bb + Ar, respectively. In this application, the EF of the Bb + N treatment was higher than the others. In the second application, the FEs were drastically reduced to 0.28%; 0.31% 0.19% Deg, Bb + N and Bb + Ar, respectively. The N2O EF for urea was 4.5% and 0.4%, first and second application, respectively. The introduction of forage peanut did not alter the rate of decomposition (‘k’) of plant residues (litter) from forages. For the 6 days of grazing and the first 6 days of rest, the average ‘k’ was 0.0904 g g-1 day-1, while for the subsequent 28 days of rest it was 0.0570 g g-1 day-1. The proportion of forage peanut in the litter varied between 1 and 7%. The addition of N via BNF to the litter was 10.6 kg N ha-1 year-1. The introduction of forage peanuts is promising for milk production. There was an increase in NH3 emissions from Bb + Ar excreta and a decrease in N2O emissions. Under the conditions evaluated the mixed grass/legume pasture was more sustainable than nitrogen fertilization. BNF was able to supply the demand for N. The intensity of GHG emissions (excluding enteric methane) dropped from 470 g CO2eq to 70 g CO2eq kg of milk-1 when the N fertilizer was replaced by forage peanut.en
dc.contributor.advisor1Boddey, Robert Michael-
dc.contributor.advisor1IDhttps://orcid.org/0000-0003-3648-9859pt_BR
dc.contributor.advisor1Latteshttp://lattes.cnpq.br/0277415539607307pt_BR
dc.contributor.advisor-co1Alves, Bruno José Rodrigues-
dc.contributor.advisor-co1IDhttps://orcid.org/0000-0002-5356-4032pt_BR
dc.contributor.advisor-co1Latteshttp://lattes.cnpq.br/5238072607952859pt_BR
dc.contributor.referee1Alves, Bruno José Rodrigues-
dc.contributor.referee1IDhttps://orcid.org/0000-0002-5356-4032pt_BR
dc.contributor.referee1Latteshttp://lattes.cnpq.br/5238072607952859pt_BR
dc.contributor.referee2Pinheiro, Érika Flávia Machado-
dc.contributor.referee2IDhttps://orcid.org/0000-0001-9039-4127pt_BR
dc.contributor.referee2Latteshttp://lattes.cnpq.br/8101589624388403pt_BR
dc.contributor.referee3Campos, David Vilas Boas de-
dc.contributor.referee3Latteshttp://lattes.cnpq.br/4727714816313596pt_BR
dc.contributor.referee4Oliveira, Octavio Costa de-
dc.contributor.referee4IDhttps://orcid.org/0000-0002-8105-0055pt_BR
dc.contributor.referee4Latteshttp://lattes.cnpq.br/5024888889516530pt_BR
dc.creator.Latteshttp://lattes.cnpq.br/5248574790920884pt_BR
dc.publisher.countryBrasilpt_BR
dc.publisher.departmentInstituto de Agronomiapt_BR
dc.publisher.initialsUFRRJpt_BR
dc.publisher.programPrograma de Pós-Graduação em Agronomia - Ciência do Solopt_BR
dc.relation.referencesABIEC – Associação Brasileira das Indústrias Exportadoras de Carnes. Perfil da Pecuária no Brasil, 2019. ALEXANDRATOS, N. AND BRUINSMA. J. World agriculture towards 2030/2050: the 2012 revision. ESA Working paper No. 12-03. Rome, FAO. 2012. ALVES, N. G. Fatores determinantes da produção de leite. 1a ed. Curso de Pós-Graduação “Lato Sensu” (Especialização) a Distância – Bovinocultura Leiteira: Manejo, Mercado e Tecnologia. Lavras: UFLA/FAEPE, 41p. 2008. ALVES, B. J. R.; SMITH, K. A.; FLORES, R. A.; CARDOSO, A. S.; OLIVEIRA, W. R. D.; JANTALIA, C. P. J; URQUIAGA, S.; BODDEY, R. M. Selection of the most suitable sampling time for static chambers for the estimation of daily mean N2O flux from soils. Soil Biology and Biochemistry, 46, 129-135, 2012. ARAÚJO, E. S.; MARSOLA, T.; MIYAZAWA, M.; SOARES, L. H. B.; URQUIAGA, S.; BODDEY, R. M.; ALVES, B. J. R. Calibração de câmara semiaberta estática para quantificação de amônia volatilizada do solo. Pesquisa. Agropecuária. Brasileira. v. 44, p. 769 – 776. 2009. ARNOLD, S L & SCHEPERS, J S. A simple roller-mill grinding procedure for plant and soil samples. Communications in Soil Science and Plant Analysis, v.35, p.537-545, 2004 BARCELLOS, A. D. O.; RAMOS, A. K. B.; VILELA, L.; JUNIOR, M.; BUENO, G. Sustentabilidade da produção animal baseada em pastagens consorciadas e no emprego de leguminosas exclusivas, na forma de banco de proteína, nos trópicos brasileiros. Revista Brasileira de Zootecnia, v. 37 p. 51 - 67. 2008. BARNARD, R.; LEADLEY, P. W.; HUNGATE, B. A. Global change, nitrification, and denitrification: a review. Global Biogeochemical Cycles, v. 19, n. 1, 2005. BARNEZE, A.; MAZZETTO, A.; ZANI, C.; MISSELBROOK, T.; CERRI, C. Nitrous oxide emissions from soil due to urine deposition by grazing cattle in Brazil. Atmospheric Environment, v.92, p. 394 – 397. 2014. BODDEY, R. M.; REZENDE, C. P.; PEREIRA, J. M.; CANTARUTTI, R. B.; ALVES, B. J. R.; FERREIRA, E.; RICHTER, M.; CADISCH, G.; URQUIAGA, S. The nitrogen cycle in pure grass and grass/legume pastures: Evaluation of pasture sustainability. In Nuclear Techniques in Soil-Plant Studies for Sustainable Agriculture and Environmental Preservation, pp. 307 - 319. FAO/IAEA, 1995. BODDEY, R. M.; RAO, I. M.; THOMAS, R. J. Nutrient cycling and environmental impact of Brachiaria pastures. In: JW Miles, BL Maass & CB do Valle (eds) Brachiaria: The Biology, Agronomy and Improvement. pp 72 – 86. Publication 259, CIAT, Cali, Colombia. 1996. BODDEY, R. M.; MACEDO, R.; TARRÉ, R. M.; FERREIRA, E.; OLIVEIRA, O. C. DE; REZENDE, C. DE P.; CANTARUTTI, R. B.; PEREIRA, J. M.; ALVES, B.J.R.; URQUIAGA, S. Nitrogen cycling in Brachiaria pastures: the key to understanding the process of pasture decline. Agriculture, Ecosystems & Environment, v. 103, n. 2, p. 389 - 403. 2004. BOUWMAN, A. F.; BOUMANS, L. J. M.; BATJES, N. H. Estimation of global NH3 volatilization loss from synthetic fertilizers and animal manure applied to arable lands and grasslands. Global Biogeochemical Cycles, v. 16, n. 2, p. 8-1-8-14, 2002. 92 BRAZ, S. P., URQUIAGA, S., ALVES, B. J., JANTALIA, C. P., GUIMARÃES, A. P., DOS SANTOS, C. A.BODDEY, R. M.. Soil carbon stocks under productive and degraded Brachiaria pastures in the Brazilian Cerrado. Soil Science Society of America Journal, v. 77 n. 3, p. 914 - 928. 2013 BREMNER, J. Determination of nitrogen in soil by the Kjeldahl method. The Journal of Agricultural Science, v. 55 n 1, 11-33. 1960. BUTTERBACH-BAHL, K.; BAGGS, E. M.; DANNENMANN, M.; KIESE, R.; ZECHMEISTER-BOLTENSTERN, S. Nitrous oxide emissions from soils: how well do we understand the processes and their controls? Philosophical Transactions of the Royal Society B: Biological Sciences v. 368, n 1621 p. 1 – 13, 2013. CAI, Y; AKIYAMA, H. Nitrogen loss factors of nitrogen trace gas emissions and leaching from excreta patches in grassland ecosystems: A summary of available data. Science of the Total Environment, v. 572, p. 185-195, 2016. CAMERON, K. C.; DI, H. J; MOIR, J. L. Nitrogen losses from the soil/plant system: a review. Annals of Applied Biology, v. 162, n. 2, p. 145-173, 2013. CANTARUTTI, R. B.; TARRÉ, R.; MACEDO, R.; CADISCH, G.; DE REZENDE, C. P.; PEREIRA, J. M.; URQUIAGA, S. The effect of grazing intensity and the presence of a forage legume on nitrogen dynamics in Brachiaria pastures in the Atlantic forest region of the south of Bahia, Brazil. Nutrient Cycling in Agroecosystems, v. 64 n. 3, p. 257 - 271. 2002. CARDOSO, A. S., BERNDT, A., LEYTEM, A., ALVES, B. J., DE CARVALHO, I. D. N., DE BARROS SOARES, L. H., BODDEY, R. M. Impact of the intensification of beef production in Brazil on greenhouse gas emissions and land use. Agricultural Systems, 143, 86 - 96. 2016 a. CARDOSO, A. S.; ALVES, B. J. R.; URQUIAGA, S.; BODDEY, R. M. Effect of volume of urine and mass of faeces on N2O and CH4 emissions of dairy-cow excreta in a tropical pasture. Animal Production Science. v. 58, n. 6, p. 1079-1086, 2016 b. CARDOSO, A S.; QUINTANA, B. G.; JANUSCKIEWICZ, E. R.; DE FIGUEIREDO BRITO, L.; DA SILVA MORGADO, E.; REIS, R. A.; RUGGIERI, A. C. N2O emissions from urine-treated tropical soil: Effects of soil moisture and compaction, urine composition, and dung addition. Catena, n. 157, p. 325 - 332. 2017 CARDOSO, A. S.; OLIVEIRA, S. C.; JANUSCKIEWICZ, E. R.; BRITO, L. F.; DA SILVA MORGADO, E.; REIS, R. A.; RUGGIERI, A. C. Seasonal effects on ammonia, nitrous oxide, and methane emissions for beef cattle excreta and urea fertilizer applied to a tropical pasture. Soil and Tillage Research, n. 194, 2019 CHAPUIS-LARDY, L.; WRAGE, N.; METAY, A.; CHOTTE, J.; BERNOUX, M. Soils, a sink for N2O? A review. Global Change Biology, v. 13, p. 1-17, 2007. CHIZZOTTI, M. L.; VALADARES FILHO, S. D. C.; VALADARES, R. F. D.; CHIZZOTTI, F. H. M.; MARCONDES, M. I.; FONSECA, M. A. Consumo, digestibilidade e excreção de ureia e derivados de purinas em vacas de diferentes níveis de produção de leite. Revista Brasileira de Zootecnia, v. 36 n. 1, p. 138 - 146. 2007. COATES, D. B.; SCHACHENMANN, P.; JONES, R. J. Reliability of extrusa samples collected from steers fistulated at the oesophagus to estimate the diet of resident animals in grazing experiments. Australian Journal of Experimental Agriculture, v. 27, n. 6, p. 739- 745, 1987. 93 DAVIDSON, E. A.; KELLES, M.; ERICKSON, H. E.; VERCHOT, L. V.; VELDKAMP, E. Testing a Conceptual Model of Soil Emissions of Nitrous and Nitric Oxides. Bioscience, v. 50, no 8, p. 667 - 680, 2000. DEWHURST, R. J.; FISHERW. J.; TWEED, J. K. S.; WILKINS R. J. Comparison of grass and legume silages for milk production. 1. Production responses with different levels of concentrate. Journal of Dairy Science, 86, p. 2598–2611. 2003 DIJKSTRA, J.; OENEMA, O.; VAN GROENIGEN, J. W.; SPEK, J. W.; VAN VUUREN, A. M.; BANNINK, A. Diet effects on urine composition of cattle and N2O emissions. Animal. V. 7 s. 2, p. 292 - 302. 2013. DOBBIE, K. E.; SMITH, K. A. Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water‐filled pore space and other controlling variables. Global Change Biology, v. 9, n. 2, p. 204 - 218, 2003. ETTALA, T. & KREULA, M. Studies on the nitrogen compounds of the faeces of dairy cows fed urea as the sole or partial source of nitrogen. Agricultural and Food Science, v. 51 n. 1, p. 506 - 513. 1979 FERRAZ, J. B. S.; DE FELÍCIO, P. E. Production systems – An example from Brazil. Meat Science, v. 84, n. 2, p. 238-243, 2010. FIRESTONE, M. K.; DAVIDSON, E. A. Microbial basis of NO and N2O production and consumption in soils. In: ANDRAE, M. O.; SCHIMEL, D. S. (Eds.). Exchange of Trace Gases Between Terrestrial Ecosystems and the Atmosphere. New York, 7 - 21, 1989. FOOD AND AGRICULTURE ORGANIZATION OF UNITED NATIONS (FAO). World Fertilizer Trends and Outlook to 2020. Rome. 38 p. 2017. FLESSA, H.; DORSCH, P.; BEESE, F.; KONIG, H.; BOUWMAN, A. F. Influence of cattle wastes on nitrous oxide and methane fluxes in pasture land. Journal of Environmental Quality, v. 25, n. 6, p. 1366 - 1370, 1996. GERSSEN-GONDELACH, S. J.; LAUWERIJSSEN, R. B.; HAVLÍK, P.; HERRERO, M.; VALIN, H.; FAAIJ, A. P.; WICKE, B. Intensification pathways for beef and dairy cattle production systems: Impacts on GHG emissions, land occupation and land use change. Agriculture, Ecosystems & Environment, n. 240, p. 135-147. 2017 GOMES, F. K.; OLIVEIRA, M. D.; HOMEM, B. G.; BODDEY, R. M.; BERNARDES, T. F.; GIONBELLI, M. P.; CASAGRANDE, D. R. Effects of grazing management in Brachiaria grass-forage peanut pastures on canopy structure and forage intake. Journal of Animal Science, v. 96 n. 9, p. 3837 - 3849. 2018. GONZALEZ, M. S.; NEURKVAN, L. M.; ROMERO, F. Producion de leche en pasturas de estrella africana (Cynodon nlemfluensis) solo y associado con Arachis pintoi o Desmodium ovalifolium. Pasturas Tropicales, v. 18, n. 1, p. 2 - 12. 1996. van GROENIGEN, J. W.; VELTHOF, G. L.; VAN DER BOLT, F. J.; VOS, A., KUIKMAN, P. J. Seasonal variation in N2O emissions from urine patches: effects of urine concentration, soil compaction and dung. Plant and Soil, v. 273 n. (1-2), 15-27. 2005. HAYNES, R. J.; WILLIAMS, P. H. Nutrient cycling and soil fertility in the grazed pasture ecosystem. Advances in Agronomy, v. 49, p. 119 - 199, 1993. HERNANDEZ, C. H. M.; ARGEL, M. P. J.; IBRAHIM, M. A.; MANNETJE, L. T. Pasture production, diet selection and liveweight gains of cattle grazing Brachiaria brizantha with or without Arachis pintoi at two stocking rates in the Atlantic Zone of Costa Rica. Tropical Grasslands. 1995. 94 HUHTANEN, P.; KAUSTELL, K.; JAAKKOLA, S. The use of internal markes to predict total digestibility and duodenal flow of nutrients in cattle given six different diets. Animal Feed Science and Technology, v. 48, p. 211 - 227, 1994. JAFFÉ, M. Ueber den Niederschlag, welchen Pikrinsäure in normalem Harn erzeugt und über eine neue Reaction des Kreatinins. Zeitschrift für physiologische Chemie, v. 10 n. 5, p. 391 - 400. 1886. JANTALIA, C. P.; HALVORSON, A. D.; FOLLETT, R. F.; ALVES, B. J. R.; POLIDORO, J. C.; URQUIAGA, S. Nitrogen source effects on ammonia volatilization as measured with semi-static chambers. Agronomy Journal, n. 104 p. 1595-1603, 2012. IBGE, Instituto Brasileiro de Geografia e Estatística, Censo Agropecuário. Disponível em <https://sidra.ibge.gov.br/pesquisa/censo-agropecuario/censo-agropecuario-2017>. Acesso Janeiro de 2019. IBGE, Instituto Brasileiro de Geografia e Estatística, Pesquisa Pecuária Municipal. Disponível em <https://sidra.ibge.gov.br/pesquisa/ppm/quadros/brasil/2018> Acesso em Janeiro de 2019. IPCC (Intergovernmental Panel on Climate Change). Guidelines for National Greenhouse Gas Inventories. Global Environmental Strategies (IGES), Hayama, Kanagawa, Japan. 2006. IPCC, Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Stocker, T. F., D. Qin, G.-K. Plattner, M. Tignor, S. K. Allen, J. Boschung, A. Nauels, Y. Xia, V. Bexand P.M. Midgley (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA, 1535 pp. 2013. IPCC, Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp. 2014. IPNI International Plant Nutrition Institute. Consumo de fertilizantes. acesso dezembro de 2019 <http://brasil.ipni.net/article/BRS-3132>. 2019 JONES, R J; LUDLOW, M M; TROUGHTON, J H; BLUNT, C G. Estimation of the proportion of C3 and C4 plant species in the diet of animals from the ratio of natural 12C and 13C isotopes in the faeces. Journal of Agricultural Science, v.92, n.1, p. 91 - 100, 1979. KEBREAB, E.; FRANCE, J.; BEEVER, D. E.; CASTILLO, A. R. Nitrogen pollution by dairy cows and its mitigation by dietary manipulation. Nutrient Cycling in Agroecosystems. v. 60, p. 275 – 285. 2001. KEMPERS, A. J.; ZWEERS, A. Ammonium determination in soil extracts by the salicylate method. Communications in Soil Science and Plant Analysis, v. 17, n. 7, p. 715-723, 1986. de KLEIN, C. A. M. Review of the N2O emission factor for excreta deposited by grazing animals (EF3prp). In ‘Paper prepared as part of the 2006 revised guidelines for greenhouse gas inventories of IPCC’. (Eds J Luo, T Van Der Weerden, C Hoogendoom, CAM De Klein) pp. 30–41. (Ministry of Agriculture and Forestry: Wellington). 2004. LABORATÓRIO DE PROCESSAMENTO DE IMAGENS E GEOPREOCESSAMENTO Universidade Federal de Goiás. LAPIG/UFG. Atlas Digital das Pastagens Brasileiras. 2019. LESSA A. C. R.; MADARI, B. E.; PAREDES, D. S.; BODDEY, R. M.; URQUIAGA, S.; JANTALIA, C. P.; ALVES B. J. R. Bovine urine and dung deposited on Brazilian savannah 95 pastures contribute differently to direct and indirect soil nitrous oxide emissions. Agriculture, Ecosystems and Environment. n. 103. 2014. LINN, D. M.; DORAN J. W. Effect of water-filled pore space on carbon dioxide and nitrous oxide production in tilled and no tilled soils. Soil Science Society American Journal, v. 48, p. 1267 - 1272, 1984. LINN, J, G; Factors Affecting the Composition of Milk from Dairy Cows in: Designing Foods: Animal Product Options in the Marketplace, Committee on Technological Options to Improve the Nutritional Attributes of Animal Products, National Research Council 1988. LUO, J.; BALVERT, S. F.; WISE, B.; WELTEN, B.; LEDGARD, S. F.; DE KLEIN, C. A. M.; JUDGE, A. Using alternative forage species to reduce emissions of the greenhouse gas nitrous oxide from cattle urine deposited onto soil. Science of the Total Environment, n. 610, p. 1271 - 1280. 2018. MARTHA, G. B.; ALVES, E.; CONTINI, E. Land-saving approaches and beef production growth in Brazil. Agricultural Systems, v. 110, p. 173-177, 2012. MATHIEU, O.; HENAULT, C.; LEVEQUE, J.; BAUJARD, E.; MILLOUX, M. J.; ANDREUX, F. Quantifying the contribution of nitrification and denitrification to the nitrous oxide flux using N-15 tracers. Environmental Pollution v. 144, p. 933 – 940. 2006. MAZZETTO, A. M.; BARNEZE, A. S.; FEIGL, B. J.; VAN GROENIGEN, J. W.; OENEMA, O.; CERRI, C. C. Temperature and moisture affect methane and nitrous oxide emission from bovine manure patches in tropical conditions. Soil Biology and Biochemistry, n. 76, p. 242 - 248. 2014. MAZZETTO, A. M.; BARNEZE, A. S.; FEIGL, B. J.; VAN GROENIGEN, J. W.; OENEMA, O.; DE KLEIN, C. A. M.; CERRI, C. C. Use of the nitrification inhibitor dicyandiamide (DCD) does not mitigate N2O emission from bovine urine patches under Oxisol in Northwest Brazil. Nutrient cycling in agroecosystems, n. 101 v. 1, p. 83 - 92. 2015. MINISTÉRIO DA CIÊNCIA, TECNOLOGIA, INOVAÇÕES E COMUNICAÇÕES (MCTIC). Estimativas Anuais de Emissões de Gases de Efeito Estufa no Brasil. 4o Edição. 91 p. 2017. MITCHELL, J, F. B. The “greenhouse” effect and climate change. Reviews of Geophysics, v. 27, n. 1, p. 115 - 139, 1989. MIYAZAWA, M.; PAVAN, M. A.; BLOCK, M. F. Determinação espectrofotométrica de nitrato em extratos de solo sem redução química. Pesquisa Agropecuária Brasileira, v. 20, p. 129 - 133, 1985. MOSIER, A.; KROEZE, C.; NEVISON, C.; OENEMA, O.; SEITZINGER, S.; VAN CLEEMPUT, O. Closing the global N2O budget: nitrous oxide emissions through the agricultural nitrogen cycle. Nutrient cycling in Agroecosystems, n. 52, v. 2, p. 225 - 248. 1998. MULVANEY, M. J.; CUMMINS, K. A.; WOOD, C.; WOOD, B. H.; TYLER, P. J. Ammonia emissions from field-simulated cattle defecation and urination. Journal of environmental quality, n. 37, v. 6, p. 2022 - 2027. 2008. MYERS, W.D.; LUDDEN, P.A.; NAYIGIHUGU, V.; HESS, B.W. Technical Note: a procedure for the preparation and quantitative analysis of samples for titanium dioxide. Journal of Animal Science, v.82, n.1, p.179 - 183, 2004. 96 MYHRE, G. D.; SHINDELL, F.-M.; BRÉON, W.; COLLINS, J.; FUGLESTVEDT, J.; HUANG, D.; KOCH, J.-F.; LAMARQUE, D.; LEE, B.; MENDOZA, T.; NAKAJIMA, A.; ROBOCK, G.; STEPHENS, T.; TAKEMURA; H. ZHANG. Anthropogenic and Natural Radiative Forcing. In: Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Stocker, T.F., D. Qin, G.-K. Plattner, M. Tignor, S.K. Allen, J. Boschung, A. Nauels, Y. Xia, V. Bex and P.M. Midgley (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA. 2013. OENEMA, O.; VELTHOF, G. L.; YAMULKI, S.; JARVIS, S. C. Nitrous oxide emissions from grazed grassland. Soil use and Management, v. 13, p. 288 - 295, 1997. OKITO, A.; ALVES, B. J. R.; URQUIAGA, S.; BODDEY, R. M. Isotopic fractionation during N2 fixation by four tropical legumes. Soil Biology & Biochemistry, v. 36, n. 7, p. 1179 - 1190, 2004. OLIVEIRA, C., SCOTTI, M. R. M. M. L., PURCINO, H., VASCONCELLOS, C., MARRIEL, I., SÁ, N. Decomposition of Arachis pintoi litter intercropped with forage grass in “Cerrado” soil in the dry and wet seasons. Biology and Fertility of soils, v. 36, n. 6, p. 405 - 410. 2002. ONU. United Nations World Population Prospects: The 2010 Revision. 2011. PAN, B.; LAM, S. K.; MOSIER, A.; LUO, Y.; CHEN, D. Ammonia volatilization from synthetic fertilizers and its mitigation strategies: a global synthesis. Agriculture, Ecosystems & Environment, v. 232, p. 283 - 289. 2016. PARIS, W.; CECATO, U.; DOS SANTOS, G. T.; BARBEIRO, L.; AVANZZO, L.; LIMÃO, V. Produção e qualidade de massa de forragem nos estratos da cultivar coastcross-1 consorciada com Arachis pintoi com e sem adubação nitrogenada. Acta Scientiarum. Animal Sciences, v. 30 n. 2, p. 135 - 143. 2008. PARIS, W.; CECATO, U.; BRANCO, A. F.; BARBERO, L. M.; GALBEIRO, S. Produção de novilhas de corte em pastagem de Coastcross-1 consorciada com Arachis pintoi com e sem adubação nitrogenada. Revista Brasileira de Zootecnia, v.38. n. 1, p.122 - 129. 2009. PEREIRA, J. M.; REZENDE, C. P.; BORGES, A. M. F.; HOMEM, B. G. C.; CASAGRANDE, D. R.; MACEDO, T. M.; ALVES, B. J. R.; SANT’ANNA, S. A. C.; URQUIAGA, S.; BODDEY, R. M. Production of Beef Cattle grazing on Brachiaria brizantha (Marandu grass) – Arachis pintoi (forage peanut cv. Belomonte) mixture exceeded that on grass monocultures fertilized with 120 kg N/ha. Grass forage Science. V. 75 p. 28 – 36. 2020. PETERSEN, S. O.; SOMMER, S. G.; AAES, O.; SØEGAARD, K. Ammonia losses from urine and dung of grazing cattle: effect of N intake. Atmospheric Environment, n. 32 v. 3, p. 295-300. 1998. PHELAN, P.; MOLONEY, A. P.; MCGEOUGH, E. J.; HUMPHREYS, J.; BERTILSSON, J.; O’RIORDAN, E. G.; O’KIELY, P. Forage legumes for grazing and conserving in ruminant production systems. Critical Reviews in Plant Sciences, v. 34, p. 1 – 46. 2015 POTH, M.; FOCHT, D. D. 15N kinetic analysis of N2O production by Nitrosomonas europaea: an examination of nitrifier denitrification. Applied. Environment. Microbiology., v. 49, n. 5, p. 1134-1141, 1985. RAMALHO, I. O., REZENDE, C. D. P., PEREIRA, J. M., MACEDO, R. D. O., SANTOS, C. A. D., MONTEIRO, R. C., BODDEY, R. M. Deposition and decomposition of litter in 97 periods of grazing and rest of a tropical pasture under rotational grazing. Ciência Rural, n. 49 p. 12. 2019. R CORE TEAM. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. 2019 REED, K. F.; MORAES, L. E.; CASPER, D. P.; KEBREAB, E. Predicting nitrogen excretion from cattle. Journal of Dairy Science, v. 98, p. 3025 - 3035, 2015. REZENDE, C.P., R.B. CANTARUTTI, J.M. BRAGA, J.A. GOMIDE, E. FERREIRA, R. TARRÉ, R. MACEDO, B.J.R. ALVES, S. URQUIAGA, G. CADISCH, K.E. GILLER, AND R.M. BODDEY. Litter deposition and disappearance in Brachiaria pastures in the Atlantic forest region of the South of Bahia, Brazil. Nutrient Cycling in Agroecosystems n. 54: p. 99 – 112. 1999. RIBEIRO FILHO, H. M. N.; DELAGARDE, R.; PEYRAUD, J. L. Inclusion of white clover in strip-grazed perennial ryegrass swards: herbage intake and milk yield of dairy cows at different ages of sward regrowth. Animal Science. v 77 n. 3. p. 499 – 510. 2003. RIBEIRO FILHO, H. M. N., DELAGARDE, R., PEYRAUD, J. L. Herbage intake and milk yield of dairy cows grazing perennial ryegrass swards or white clover/perennial ryegrass swards at low- and medium-herbage allowances. Animal Feed Science Technology. v. 119. p. 13 – 27. 2005. ROBERTSON, G. PHILIP; GRACE, PETER R. Greenhouse gas fluxes in tropical and temperate agriculture: the need for a full-cost accounting of global warming potentials. In: Tropical Agriculture in Transition - Opportunities for Mitigating Greenhouse Gas Emissions? Springer, Dordrecht. p. 51 - 63. 2004. ROCHETTE, P.; ANGERS, D. A.; CHANTIGNY, M. H.; GASSER, M. O.; MACDONALD, J. D.; PELSTER, D. E.; BERTRAND, N. NH3 volatilization, soil concentration and soil pH following subsurface banding of urea at increasing rates. Canadian Journal of Soil Science , n. 93, v. 2, p. 261 - 268. 2013. RUSER, R.; FLESSA, H.; RUSSOW, R.; SCHMIDT, G.; BUEGGER, F.; MUNCH, J. C. Emission of N2O, N2 and CO2 from soil fertilized with nitrate: effect of compaction, soil moisture and rewetting. Soil Biology & Biochemistry, 38, 263–274, 2006. Sampaio, I. B. M. Estatística aplicada à experimentação animal. 2. ed. Belo Horizonte: FEPMVZ, 265 p., 2002. SANTOS, C. A. dos; REZENDE, C. de P.; PINHEIRO, E. F. M.; PEREIRA, J. M.; ALVES, B. J. R.; URQUIAGA, S.; BODDEY, R. M. Changes in soil carbon stocks after land-use change from native vegetation to pastures in the Atlantic forest region of Brazil. Geoderma. V. 337. P. 394 – 401. 2019. SARVVL, B. A. I.; CAO, Z. J.; XIN, J. I. N.; WANG, Y. J.; YANG, H. J.; LI, S. L. The effects of step-wise improvement of forage combination in total mixed rations on fatty acid profile in the rumen and milk of Holstein cows. Journal of Integrative Agriculture, v. 17, n. 8, p. 1833 - 1842. 2018. SCHLESINGER, W.H. An Estimate of the Global Sink for Nitrous Oxide in Soils. Global Change Biology, v. 19, p. 2929 - 2931, 2013. SCHIRMANN, J.; DE BASTOS, D. F.; WEILER, D. A.; VELOSO, M. G.; DIECKOW, J.; DE FACCIO CARVALHO, P. C.; BAYER, C. Nitrous oxide emission factor from cattle urine and dung in native grassland of the Pampa biome, South Brazil. Soil Research. 2019. 98 SENGER, C. C.; KOZLOSKI, G. V.; SANCHEZ, L. M. B.; MESQUITA, F. R.; ALVES, T. P.; CASTAGNINO, D. S. Evaluation of autoclave procedures for fibre analysis in forage and concentrate feedstuffs. Animal Feed Science and Technology, v. 146, n. 1-2, p. 169-174, 2008. SILVA, H. M., BATISTA DUBEUX, J. C., FERREIRA DOS SANTOS, M. V., DE ANDRADE LIRA, M., MUIR, J. P. Signal grass litter decomposition rate increases with inclusion of calopo. Crop Science. v. 52 n. 3. p. 1416 - 1423. 2012. SIMON, P. L.; DIECKOW, J.; DE KLEIN, C. A.; ZANATTA, J. A.; VAN DER WEERDEN, T. J.; RAMALHO, B.; BAYER, C. Nitrous oxide emission factors from cattle urine and dung, and dicyandiamide (DCD) as a mitigation strategy in subtropical pastures. Agriculture, Ecosystems & Environment, n. 267, p. 74 - 82. 2018. SINGH, J.; KUNHIKRISHNAN, A.; BOLAN, N. S.; SAGGAR, S. Impact of urease inhibitor on ammonia and nitrous oxide emissions from temperate pasture soil cores receiving urea fertilizer and cattle urine. Science of the total Environment, n.465, p.56 - 63. 2013. SISTEMA BRASILEIRO DE CLASSIFICAÇÃO DE SOLOS (SiBCS), EMBRAPA, 5a edição, Brasília, 2018. SMITH, K. A.; DOBBIE, K. E.; THORMAN, R.; WATSON, C. J.; CHADWICK, D. R.; YAMULKI, S.; BALL, B. C. The effect of N fertilizer forms on nitrous oxide emissions from UK arable land and grassland. Nutrient cycling in Agroecosystems, n. 93 v.2, 127-149. 2012. SOMMER, S. G. & HUTCHINGS, N. J. Ammonia emission from field applied manure and its reduction. European journal of agronomy, n. 15 v.1, p.1 - 15. 2001 SOMMER, S. G., SCHJOERRING, J. K., DENMEAD, O. T. Ammonia emission from mineral fertilizers and fertilized crops. Advances in agronomy, n. 82, v. 4. 2004. SORDI, A.; DIECKOW, J.; BAYER, C.; ALBUQUERQUE, M. A. Nitrous oxide emission factors for urine and dung patches in a subtropical Brazilian pastureland. Agriculture Ecosystems Environment, v. 190, p. 94 - 103, 2013. TAN, I. Y. S.; VAN, E. S. H. M.; DUXBURY, J. M.; MELKONIAN J.J.; SCHINDELBECK, R.R.; GEOHRING, L. D.; HIVELY, W. D.; MOEBIUS B. N. Single-event Nitrous Oxide Losses under Maize Production as Affected by Soil Type, Tillage, Rotation, and Fertilization. Soil and Tillage Research, Amsterdam, v. 102, n. 1, p. 19-26, 2009. TAMELE, O. H.; LOPES DE SÁ, O. A. A.; BERNARDES, T. F.; LARA, M. A. S.; CASAGRANDE, D. R. Optimal defoliation management of Brachiaria grass–forage peanut for balanced pasture establishment. Grass and Forage Science, v.73 n.2, p. 522 - 531. 2017. TARRÉ, R. M.; MACEDO, R.; CANTARUTTI, R. B.; REZENDE, C. P.; PEREIRA, J. M.; FERREIRA, E.; ALVES, B.J.R.; URQUIAGA, S.; BODDEY, R. M. The effect of the presence of a forage legume on nitrogen and carbon levels in soils under Brachiaria pastures in the Atlantic forest region of the south of Bahia, Brazil. Plant and Soil. v. 234. n. 1. p. 15 - 26. 2001. TEKERLI, M.; AKINCI, Z.; DOGAN, I.; AKCAN, A. Factors affecting the shape of lactation curves of Holstein cows from the Balikesir province of Tukey. Journal of Dairy Science, v. 83, n.6, p.1381- 1386, 2000. THOMAS, R. J.; ASAKAWA, N. M. Decomposition of leaf litter from tropical forage grasses and legumes. Soil Biology and Biochemistry, v. 25, n. 10, p. 1351-1361, 1993. 99 TITGEMEYER, E. C.; ARMENDARIZ, C. K.; BINDEL, D. J. Evaluation of titanium dioxide as a digestibility marker for cattle. Journal of Animal. Science, v.79, p.1059 - 1063, 2001. TUBIELLO, F. N.; SALVATORE, M.; ROSSI, S.; FERRARA, A.; FITTON, N.; SMITH, P. The FAOSTAT database of greenhouse gas emissions from agriculture. Environmental Research Letters, v. 8 n. 1, p. 15009. 2013. VALLIS, I.; HARPER, L. A.; CATCHPOOLE, V. R.; WEIER, K. L. Volatilization of ammonia from urine patches in a subtropical pasture. Australian Journal of Agricultural Research, n. 33 v.1, p. 97 - 107. 1982. VAN DER WEERDEN, T. J.; LUO, J.; KLEIN, C. A. M.; HOOGENDOORN, C. J.; LITTLEJOHN, R. P.; RYS, G. J. Disaggregating nitrous oxide emission factors for ruminant urine and dung deposited onto pastoral soils. Agriculture Ecosystems & Environment. 141, 426 – 436. 2011. WANG, C.; YUNG, Y.; LACIS, A. M. O. T.; HANSEN, J. Greenhouse effects due to man- made perturbations of trace gases. Science, v. 194, n. 4266, p. 685 - 690, 1976. WILD, M.; FOLINI, D.; SCHAR, C.; LOEB, N.; DUTTON, E.; KONIG-LANGLO. The global energy balance from a surface perspective. Climate dynamics, v. 40, n. 11 - 12, p. 3107 - 3134, 2013. WOOD, P. D. P. Algebraic model of the lactation curve in cattle. Nature. v. 216, p. 164-165, 1967. WORLD METEREOLOGICAL ORGANIZATION (WMO). Greenhouse gas bulletin No 14. The State of Greenhouse Gases in the Atmosphere Based on Global Observations through 2017. 4 p. 2018. WU, D.; DONG, W.; OENEMA, O.; WANG, Y.; TREBS, I.; HU, C. N2O consumption by low-nitrogen soil and its regulation by water and oxygen. Soil Biology and Biochemistry, v.60, p.165-172. 2013. XAVIER, D. F., DA SILVA LÉDO, F. J., PACIULLO, D. S. C., URQUIAGA, S., ALVES, B. J., BODDEY, R. M. Nitrogen cycling in a Brachiaria-based silvopastoral system in the Atlantic forest region of Minas Gerais, Brazil. Nutrient Cycling in Agroecosystems, v. 99, n. 13, p. 45 – 62. 2013. YAMULKI, S.; JARVIS, S. C.; OWEN, P. Nitrous oxide emissions from excreta applied in a simulated grazing pattern. Soil Biology Biochemistry. v. 30 p. 491 – 500. 1998. ZAMAN, M.; NGUYEN, M. L.; MATHESON, F.; BLENNERHASSETT, J. D.; QUIN, B. F. Can soil amendments (zeolite or lime) shift the balance between nitrous oxide and dinitrogen emissions from pasture and wetland soils receiving urine or urea-N? Soil Research, v. 45 n. 7, p. 543 - 553. 2007. ZAMAN, M.; ZAMAN, S.; NGUYEN, M. L.; SMITH, T. J.; NAWAZ, S. The effect of urease and nitrification inhibitors on ammonia and nitrous oxide emissions from simulated urine patches in pastoral system: A two-year study. Science of the total Environment, v. 465, p. 97 - 106. 2013. ZHANG, J.; MUELLER, C.; CAI, Z. Heterotrophic nitrification of organic N and its contribution to nitrous oxide emissions in soils. Soil Biology and Biochemistry, v. 84, p. 199 - 209, 2015.pt_BR
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