899 resultados para BRACHIARIA-BRIZANTHA
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Pós-graduação em Agronomia - FEIS
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Pós-graduação em Agronomia (Ciência do Solo) - FCAV
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Pós-graduação em Agronomia - FEIS
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Pós-graduação em Agronomia (Agricultura) - FCA
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Pós-graduação em Agronomia (Agricultura) - FCA
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Introduction: In recent years, hantavirus infections producing severe diseases have obtained an increased attention from public health authorities from the countries of Eurasia to the Americas. Brazil has reported 1,300 cases of hantavirus cardiopulmonary syndrome (HCPS) from 1993 to 2010, with about 80 of them occurring in the northeast of the state of Sao Paulo, with 48% fatality rate. Araraquara virus was the causative agent of HCPS in the region. Considering that hantaviruses causing human disease in the Americas were unknown until 1993, we have looked for hantavirus infections in the population of Cassia dos Coqueiros county, northeast of the state of Sao Paulo, Brazil, before this time. This county has about 2,800 inhabitants and an economy based on agriculture, including cultivation of Brachiaria decumbens grass. The grass seeds are an important rodent attraction, facilitating transmission of hantavirus to man. Four HCPS cases were reported so far in the county. Methods: In this study, 1,876 sera collected from 1987 to 1990 were tested for IgG to hantavirus by IgG-ELISA, using the N recombinant protein of Araraquara virus as antigen. Results: Positive results were observed in 89 (4.7%) samples, which were all collected in 1987. The positivity among urban inhabitants was 5.3%, compared with 4.3% among those living in rural areas. Conclusions: Our results showed that hantavirus infections occurred in Cassia dos Coqueiros, completely unrecognized, even before hantaviruses were described in the Americas.
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Previous studies showed that Santa Ines (SI) hair sheep were more resistant to gastrointestinal nematode infections (GIN) than Ile de France (IF) sheep. The present experiment aimed to evaluate if that reported resistance difference against GIN also occurred against Oestrus ovis infestation and also to evaluate the influence of O. ovis infestation on the gastrointestinal nematodes (GIN) infections. SI (n = 12) and IF (n = 12) young male lambs were weaned at 2 months of age and moved to a paddock (0.3 ha) with Brachiaria decumbens grass, where they also received concentrate ration. The animals were kept together during the experimental period (September to early December 2009). Fecal and blood samples were taken from all animals every 2 weeks and body weight and nasal discharge score (oestrosis clinic signs) were recorded on the same occasion. In early December 2009, all lambs were sacrificed and O. ovis larvae and GIN were recovered, counted and identified according to the larval stage. All animals were infested by different larval instars of O. ovis without any statistical difference between breeds (P > 0.05). The SI lambs had an average of 24.8 larvae, and the intensity of infection ranged between 14 and 39 larvae, while the IF lambs showed an average of 23.5 larvae with the minimum and maximum from 11 to 36 larvae, respectively. SI lambs presented the lowest nematode fecal egg counts (FECs) and the lowest mean numbers of Haemonchus contort us, Trichostrongylus colubriformis and Strongyloides papillosus, however, there was no significant differences between group means (P > 0.05). Inverse relationship between numbers of O. ovis larvae and gastrointestinal nematodes was observed in both breeds. SI sheep showed a significant increase in blood eosinophils and total IgE serum levels and these variables were negatively correlated with nematode FEC. A negative correlation was observed between total IgE serum level and H. contortus burden in both breeds. In conclusion, there was no breed difference regarding O. ovis infestation and in each breed, animals with more nasal bot fly larvae tended to display smaller worm burden. (C) 2011 Elsevier B.V. All rights reserved.
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Soil sulfur (S) partitioning among the various pools and changes in tropical pasture ecosystems remain poorly understood. Our study aimed to investigate the dynamics and distribution of soil S fractions in an 8-year-old signal grass (Brachiaria decumbens Stapf.) pasture fertilized with nitrogen (N) and S. A factorial combination of two N rates (0 and 600?kg N ha1 y1, as NH4NO3) and two S rates (0 and 60?kg S ha1 y1, as gypsum) were applied to signal grass pastures during 2 y. Cattle grazing was controlled during the experimental period. Organic S was the major S pool found in the tropical pasture soil, and represented 97% to 99% of total S content. Among the organic S fractions, residual S was the most abundant (42% to 67% of total S), followed by ester-bonded S (19% to 42%), and C-bonded S (11% to 19%). Plant-available inorganic SO4-S concentrations were very low, even for the treatments receiving S fertilizers. Low inorganic SO4-S stocks suggest that S losses may play a major role in S dynamics of sandy tropical soils. Nitrogen and S additions affected forage yield, S plant uptake, and organic S fractions in the soil. Among the various soil fractions, residual S showed the greatest changes in response to N and S fertilization. Soil organic S increased in plots fertilized with S following the residual S fraction increment (16.6% to 34.8%). Soils cultivated without N and S fertilization showed a decrease in all soil organic S fractions.
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DISTRIBUTION OF NITROGEN AMMONIUM SULFATE (N-15) SOIL-PLANT SYSTEM IN A NO-TILLAGE CROP SUCCESSION The N use by maize (Zea mays, L.) is affected by N-fertilizer levels. This study was conducted using a sandy-clay texture soil (Hapludox) to evaluate the efficiency of N use by maize in a crop succession, based on N-15-labeled ammonium sulfate (5.5 atom %) at different rates, and to assess the residual fertilizer effect in two no-tillage succession crops (signalgrass and corn). Two maize crops were evaluated, the first in the growing season 2006, the second in 2007, and brachiaria in the second growing season. The treatments consisted of N rates of 60, 120 and 180 kg ha(-1) in the form of labeled N-15 ammonium sulfate. This fertilizer was applied in previously defined subplots, only to the first maize crop (growing season 2006). The variables total accumulated N; fertilizer-derived N in corn plants and pasture; fertilizer-derived N in the soil; and recovery of fertilizer-N by plants and soil were evaluated. The highest uptake of fertilizer N by corn was observed after application of 120 kg ha(-1) N and the residual effect of N fertilizer on subsequent corn and Brachiaria was highest after application of 180 kg ha(-1) N. After the crop succession, soil N recovery was 32, 23 and 27 % for the respective applications of 60, 120 and 180 kg ha(-1) N.
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Plant secondary metabolites are a group of naturally occurring compound classes biosynthesized by differing biochemical pathways whose plant content and regulation is strongly susceptible to environmental influences and to potential herbal predators. Such abiotic and biotic factors might be specifically induced by means of various mechanisms, which create variation in the accumulation or biogenesis of secondary metabolites. Hence the dynamic aspect of bioactive compound synthesis and accumulation enables plants to communicate and react in order to overcome imminent threats. This contribution aims to review the most important mechanisms of various abiotic and biotic interactions, such as pathogenic microorganisms and herbivory, by which plants respond to exogenous influences, and will also report on time-scale variable influences on secondary metabolite profiles. Transmission of signals in plants commonly occurs by 'semiochemicals', which are comprised of terpenes, phenylpropanoids, benzenoids and other volatile compounds. Due to the important functions of volatile terpenes in communication processes of living organisms, as well as its emission susceptibility relative to exogenous influences, we also present different scenarios of concentration and emission variations. Toxic effects of plants vary depending on the level and type of secondary metabolites. In farming and cattle raising scenarios, the toxicity of plant secondary metabolites and respective concentration shifts may have severe consequences on livestock production and health, culminating in adverse effects on crop yields and/or their human consumers, or have an adverse economic impact. From a wider perspective, herbal medicines, agrochemicals or other natural products are also associated with variability in plant metabolite levels, which can impact the safety and reliable efficacy of these products. We also present typical examples of toxic plants which influence livestock production using Brazilian examples of toxicity of sapogenins and alkaloids on livestock to highlight the problem. (c) 2012 Elsevier B.V. All rights reserved.
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INTRODUCTION: In recent years, hantavirus infections producing severe diseases have obtained an increased attention from public health authorities from the countries of Eurasia to the Americas. Brazil has reported 1,300 cases of hantavirus cardiopulmonary syndrome (HCPS) from 1993 to 2010, with about 80 of them occurring in the northeast of the State of São Paulo, with 48% fatality rate. Araraquara virus was the causative agent of HCPS in the region. Considering that hantaviruses causing human disease in the Americas were unknown until 1993, we have looked for hantavirus infections in the population of Cássia dos Coqueiros county, northeast of the State of São Paulo, Brazil, before this time. This county has about 2,800 inhabitants and an economy based on agriculture, including cultivation of Brachiaria decumbens grass. The grass seeds are an important rodent attraction, facilitating transmission of hantavirus to man. Four HCPS cases were reported so far in the county. METHODS: In this study, 1,876 sera collected from 1987 to 1990 were tested for IgG to hantavirus by IgG-ELISA, using the N recombinant protein of Araraquara virus as antigen. RESULTS: Positive results were observed in 89 (4.7%) samples, which were all collected in 1987. The positivity among urban inhabitants was 5.3%, compared with 4.3% among those living in rural areas. CONCLUSIONS: Our results showed that hantavirus infections occurred in Cássia dos Coqueiros, completely unrecognized, even before hantaviruses were described in the Americas.
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O aproveitamento do N pelo milho (Zea mays, L.) é influenciado pelas doses de adubo nitrogenado. O presente trabalho foi desenvolvido em um solo de textura arenoargilosa (Hapludox) e teve por objetivo avaliar a eficiência de utilização do N pela cultura de milho, em uma sucessão de culturas, utilizando-se sulfato de amônio marcado com 15N (5,5 átomos %), em diferentes doses; e o efeito residual desse fertilizante nas duas culturas subsequentes em sucessão (braquiária e milho), sob sistema plantio direto. As avaliações foram feitas em dois cultivos de milho safrinha - o primeiro no ano agrícola 2006 e o segundo em 2007 - e um de braquiária na entressafra. Os tratamentos consistiram de doses de N de 60, 120 e 180 kg ha-1, na forma de sulfato de amônio marcado (15N). Esse adubo foi aplicado em subparcelas, previamente definidas, apenas no primeiro cultivo do milho (safra 2006). Foram avaliados: N-total acumulado; N nas plantas de milho e braquiária proveniente do fertilizante, N no solo proveniente do fertilizante e recuperação de N-fertilizante pelas plantas e pelo solo. O maior aproveitamento do N-fertilizante pelo milho foi obtido no tratamento com 120 kg ha-1 de N, e o maior efeito residual do N-fertilizante pela braquiária e milho subsequente, no tratamento com 180 kg ha-1 de N. Após a sucessão de culturas, a recuperação de N pelo solo foi de 32, 23 e 27 % para os tratamentos com 60, 120 e 180 kg ha-1 de N.
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O processo de beneficiamento do zinco, extraído em Vazante pela Companhia Mineira de Metais - CMM produz um rejeito alcalino e com baixa disponibilidade de nutrientes. Esta dissertação tem como objetivo avaliar o potencial de utilização de espécies leguminosas noduladas e micorrizadas na revegetação de barragem de rejeito da CMM. Neste sentido, foram instalados dois experimentos de campo onde foi realizado o plantio prévio de Brachiaria sp. O primeiro experimento foi composto por 36 tratamentos que foram formados por uma combinação de 17 espécies + 1 testemunha (ausência de plantas) na presença e na ausência de esterco de curral (2,0 L) na cova de plantio. Cada unidade experimental foi formada por 20 exemplares da mesma espécie que foram plantadas em covas abertas manualmente (25 x 25 x 25 cm) num espaçamento de 2 x 2 m. Todas as covas receberam a adubação básica formada por 125 g de superfosfato simples e 60 g de cloreto de potássio. Entre as 17 espécies avaliadas, 3 não pertencem a família Leguminosae e receberam, além da adubação básica, cerca de 25 g de sulfato de amônio por cobertura. O segundo experimento foi montado com o objetivo de avaliar o potencial de espécies leguminosas beneficiarem o estabelecimento e crescimento de espécies não leguminosas na revegetação de barragem de rejeito da CMM. Foram utilizadas três espécies leguminosas (Enterolobium scomburkii, Acacia mangium e Acacia holosericea) e três não leguminosas (Lithraea brasiliensis, Cinnamomum glaziovii e Eugenia jambolana) num esquema fatorial (3 x 3) + 1 testemunha, formando dez tratamentos distribuídos em blocos ao acaso com três repetições. Cada parcela foi formada por 20 plantas (10 leguminosas + 10 não leguminosas) plantadas em espaçamento 2 x 2 m e com a mesma adubação básica utilizada no primeiro experimento. Todas as espécies leguminosas utilizadas foram previamente inoculadas com estirpes selecionadas de bactérias fixadoras de Nitrogênio atmosférico e com uma mistura de fungos micorrízicos provenientes da Embrapa/Agrobiologia. Os experimentos foram avaliados quanto ao estabelecimento e crescimento de plantas (altura e diâmetro do colo) aos 4, 12 e 24 meses após o plantio. Os resultados obtidos permitem concluir que dentre as espécies avaliadas, as mais indicadas para a primeira etapa da revegetação da barragem de rejeito da CMM são: Acacia holosericea, Acacia farnesiana, Acacia auriculiformis, Mimosa caesalpiniifolia, Leucaena leucocephala, Mimosa birmucronata, Enterolobium schomburkii e Prosopis juliflora. O sucesso do consórcio de espécies leguminosas e não leguminosas depende da escolha das espécies a serem combinadas, de maneira que não exista uma efetiva competição por água, nutrientes e luz que possa prejudicar as espécies de menor plasticidade. Das combinações avaliadas, as de maiores potencialidades para o programa de revegetação das barragens de rejeito da CMM são aquelas envolvendo a espécieLithraea brasiliensis.