925 resultados para PARBOILED RICE WASTEWATER
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This study evaluates the potential for using different effluents for simultaneous H-2 and CH4 production in a two-stage batch fermentation process with mixed microflora. An appreciable amount of H-2 was produced from parboiled rice wastewater (23.9 mL g(-1) chemical oxygen demand [COD]) and vinasse (20.8 mL g(-1) COD), while other effluents supported CH4 generation. The amount of CH4 produced was minimum for sewage (46.3 mL g(-1) COD), followed by parboiled rice wastewater (115.5 mL g(-1) COD) and glycerol (180.1 mL g(-1) COD). The maximum amount of CH4 was observed for vinasse (255.4 mL g(-1) COD). The total energy recovery from vinasse (10.4 kJ g(-1) COD) corresponded to the maximum COD reduction (74.7 %), followed by glycerol (70.38 %, 7.20 kJ g(-1) COD), parboiled rice wastewater (63.91 %, 4.92 kJ g(-1) COD), and sewage (51.11 %, 1.85 kJ g(-1) COD). The relatively high performance of vinasse in such comparisons could be attributed to the elevated concentrations of macronutrients contained in raw vinasse. The observations are based on kinetic parameters of H-2 and CH4 production and global energy recovery of the process. These observations collectively suggest that organic-rich effluents can be deployed for energy recovery with sequential generation of H-2 and CH4.
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Rice can easily accumulate arsenic (As) into its grain and is known to be the highest As-containing cereal. In addition, the As burden in rice may increase during its processing (such as when cooking using As-polluted water). The health risk posed by the presence of As in cooked rice depends on its release from the matrix along the digestive system (bioaccessibility). Two types of white polished long-grain rice, namely, nonparboiled and parboiled (total As: 202 and 190 mu g As kg(-1), respectively), were cooked in excess of water with different levels of As (0, 10, 47, 222, and 450 mu g As L-1). The bioaccessibility of As from these cooked rice batches was evaluated with an in vitro dynamic digestion process. Rice cooked with water containing 0 and 10 mu g As L-1 showed lower As concentrations than the raw (uncooked) rice. However, cooking water with relatively high As content (>= 47 mu g As L-1) significantly increased the As concentration in the cooked rice up to 8- and 9-fold for the nonparboiled and parboiled rice, respectively. Parboiled rice, which is most widely consumed in South Asia, showed a higher percentage of As bioaccessibility (59% to 99%) than nonparboiled rice (36% to 69%) and most of the As bioaccessible in the cooked rice (80% to 99%) was released easily during the first 2 h of digestion. The estimation of the As intake through cooked rice based on the As bioaccessibility highlights that a few grams of cooked rice (less than 25 g dry weight per day) cooked with highly As contaminated water is equivalent to the amount of As from 2 L water containing the maximum permissible limit (10 mu g As L-1).
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Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Pós-graduação em Agronomia (Proteção de Plantas) - FCA
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The present study was aimed to evaluate different (semi-solid) media for the production of Metarhizium anisopliae and Beauveria bassiana propagules, and to evaluate the tolerance of these propagules to ultraviolet radiation and temperature. The experiments were performed at the Biological Control Laboratory of the Instituto Biológico at Campinas, São Paulo, Brazil. For both fungi, 6 repetitions were performed for each of the 17 treatments: corn starch, full rice, parboiled rice, type-1 rice, type-2 rice, oat flakes, canjiquinha [grits], wheat flour, raw cassava flour, yellow corn flour, special wheat flour, corn flour, corn in grains, cassava starch, soy in grains, crushed wheat, and turf. The viability analysis was done in plastic plates containing BDA. For the bioassays involving exposure to ultraviolet light and temperature, BDA was also used for viability analysis, and each treatment was exposed to the UV radiation for 0, 25 and 50 seconds, the temperature exposure being at 20, 25, 30 and 35º C. Using a Potter tower, 2 mL of fungus suspension from each treatment was inoculated to the Diatraea saccharalis caterpillars. Regarding the sporulation, the largest concentrations of M. anisopliae and B. bassiana were found for the treatments with parboiled rice, type-1 rice, type-2 rice, yellow corn flour, corn flour and crushed wheat. The viability of all treatments was superior to 94.00%. Also, the longer the duration of the exposition to the UV, the smaller the number of fertile conidia. At 35o C, a significant loss of conidia viability was observed, and all the treatments presented some level of virulence.
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O arroz (Oryza sativa, L.), como todos os cereais, pode ser contaminado por fungos responsáveis por danos tecnológicos, nutricionais e toxicológicos, dentre eles a produção de micotoxinas. Diversas toxinas fúngicas produzidas pelo gênero Fusarium tem sido relatadas em arroz, no entanto a fumonisina B1 (FB1) é pouco estudada neste grão. As principais características da FB1 é a alta solubilidade em solventes polares, estabilidade a altas temperaturas além de efeitos neurotóxicos e carcinogênicos. Assim o objetivo deste trabalho foi avaliar o efeito do tratamento térmico e hidrotérmico nos teores de fumonisina B1 e nas características químicas de arroz comercial. Na primeira etapa do trabalho foi adaptado um método para detecção e quantificação de FB1 em arroz cru e após cocção, por HPLC-FL. O método foi avaliado quanto aos indicativos de eficiência destacando-se o LOD (30 µg.kg-1) e a recuperação ( 90% para arroz cru e 86% pra arroz cozido). Na segunda etapa realizou-se o levantamento de ocorrência de FB1 em 05 diferentes amostras comerciais de arroz integral, branco e parboilizado da cidade de Rio Grande, RS, totalizando 9 amostras. Foi detectada a presença de FB1 em 7 das 9 amostras, sendo que os maiores índices foram encontrados em amostras de arroz parboilizado e integral apresentando níveis de contaminação entre 30 e 170 µg.kg-1. A terceira etapa do trabalho consistiu no estudo do efeito de tratamentos térmicos sobre os níveis de FB1 em amostras após aplicação de calor. Foram testados tratamento hidrotérmico com evaporação, tratamento hidrotérmico com autoclavagem e tratamento térmico seco. O maior nível de redução dos teores iniciais de FB1 foi 82,8% quando se empregou tratamento térmico seco a 125 °C/3 min. Ainda foram avaliados os efeitos do t ratamento hidrotérmico com evaporação de água na composição química e na digestibilidade protéica. Esta característica proporcionou aumento de até 100% na digestibilidade in vitro das proteínas e reduziu em média 73% do teor de contaminação com FB1.
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O cultivo do arroz no RS é fortemente relacionado com recursos hídricos, pois este se faz sob irrigação e durante o beneficiamento, especialmente no caso da parboilização, são necessários volumes consideráveis de água. Em vista disso, os solutos presentes nestas águas permitem estimar o impacto desta cultura e sua industrialização na qualidade do ambiente hídrico no RS. Foi desenvolvida uma rotina analítica para caracterização físico-química das águas da cadeia produtiva do arroz, onde foram analisados nitrogênio total, nitrogênio amoniacal, nitrogênio orgânico, açucares redutores, açucares redutores totais, sólidos totais, sólidos fixos, sólidos voláteis, ácidos voláteis, alcalinidade, pH, nitrato, nitrito e fósforo. Também um método multimicotoxinas foi desenvolvido avaliando a eficiência de cinco sistemas de extração-partição para aflatoxina B1 (AFA B1), aflatoxina B2 (AFA B2), ocratoxina A (OTA), zearalenona (ZEA) e deoxinivalenol (DON). A partição liquido-liquido com clorofórmio foi a mais eficiente recuperando 89; 96; 89; 97 e 72%, respectivamente de cada micotoxina. A comparação entre volumes de solventes, onde o número de etapas envolvidas e o tempo necessário para efetuar a determinação confirmaram a simplicidade, a economia e a rapidez deste sistema de partição a ser adotado para extrair micotoxinas de água da cadeia produtiva de arroz. O método foi aplicado para determinação de micotoxinas em amostras de águas de irrigação e parboilização de arroz de diferentes procedências verificando-se que as últimas aparecem contaminadas com micotoxinas, AFA B1 9,0 ng mL-1 e DON 110 ng mL-1 . Foi realizado também um estudo de migração de micotoxinas AFA B1, OTA, ZEA e DON e outros solutos sob condições de encharcamento (4 e 6 h) em dois níveis de fortificação, durante a parboilização do grão ficando demonstrado que durante o processo ocorria a lixiviação de solutos e micotoxinas para água de encharcamento do arroz.
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Wastewater is reused and treated in four main types of farming in Vietnam: fish culture in 200 ha; rotation of rice and fish culture in 400 ha; land vegetables and aquatic vegetables.
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Eight kinds of plants were tested in channel-dyke and field irrigation systems. The removal rates of TP, phosphate, TN, ammonia, CODcr and BOD, in the channel-dyke system with napiergrass (Pennisetum purpurem Schumach, x Pennisetum alopecuroides (L.) Spreng American) were 83.2, 82.3, 76.3, 96.2, 73.5 and 85.8%, respectively. The field irrigation systems with rice I-yuanyou No.1(88-132) (Oryza sativa L.) and rice II- suakoko8 (Oryza glaberrima) had high efficiency for N removal; the removal rate were 84.7 and 84.3%, respectively. The mass balance data revealed that napiergrass, rice I and II were the most important nutrient sinks, assimilating more than 50% of TP and TN. Plant uptake of N and P as percentage of total removal from wastewater correlated with biomass yield of and planting mode. (C) 2000 Elsevier Science B.V. All rights reserved.
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Total arsenic and arsenic speciation was performed on different rice types (basmati, long-grain, polished ([white] and wholegrain [brown]) that had undergone various forms of cooking. The effect of rinse washing, low volume (2.5 : 1 water : rice) and high volume (6 : 1 water : rice) cooking, as well as steaming, were investigated. Rinse washing was effective at removing circa. 10% of the total and inorganic arsenic from basmati rice, but was less effective for other rice types. While steaming reduced total and inorganic arsenic rice content, it did not do so consistently across all rice types investigated. Low volume water cooking did not remove arsenic. High volume water : rice cooking did effectively remove both total and inorganic arsenic for the long-grain and basmati rice (parboiled was not investigated in high volume cooking water experiment), by 35% and 45% for total and inorganic arsenic content, respectively, compared to uncooked (raw) rice. To reduce arsenic content of cooked rice, specifically the inorganic component, rinse washing and high volume of cooking water are effective.