937 resultados para sunflower-oil refinery waste
Fatty acid production by four strains of Mucor hiemalis grown in plant oil and soluble carbohydrates
Resumo:
Four Mucor hiemalis strains (M1, M2, M3 and M4), isolated from soil at a depth of 0 - 15 cm in the Juréia-Itatins Ecology Station (JIES), in the state of São Paulo, Brazil and were evaluated for the production of γ-linolenic (GLA) and other unsaturated fatty acids. Five growth variables (temperature, pH, carbon source, nitrogen source, and vegetable oils) were studied. Liquid media containing 2% vegetable oil (palm oil, canola oil, soybean oil, sesame oil, or sunflower oil) or 2% carbohydrate (fructose, galactose, glycerol, glucose, lactose, maltose, sucrose, sorbitol or xylose) and 1% yeast extract as a nitrogen source were used. The greatest biomass production was observed with M3 and M4 strains in palm oil (91.5 g l -1) and sunflower oil (68.3 g l -1) media, respectively. Strain M4 produced greater quantities of polyunsaturated acids in medium containing glucose. The GLA production in the M4 biomass was 1,132.2 mg l -1 in glucose medium. Plant oils were inhibitors of fatty acid production by these strains. © 2007 Academic Journals.
Resumo:
Pós-graduação em Ciências Biológicas (Microbiologia Aplicada) - IBRC
Resumo:
Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
Resumo:
Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
Resumo:
Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
Resumo:
Sugarcane (Saccharum spp.) and palm tree (Elaeis guianeensis) are crops with high biofuel yields, 7.6 m(3) ha (1) y(-)1 of ethanol and 4 Mg ha(-1) y(-1) of oil, respectively. The joint production of these crops enhances the sustainability of ethanol. The objective of this work was comparing a traditional sugarcane ethanol production system (TSES) with a joint production system (JSEB), in which ethanol and biodiesel are produced at the same biorefinery but only ethanol is traded. The comparison is based on ISO 14.040:2006 and ISO 14044:2006, and appropriate indicators. Production systems in Cerrado (typical savannah), Cerradao (woody savannah) and pastureland ecosystems were considered. Energy and carbon balances, and land use change impacts were evaluated. The joint system includes 100% substitution of biodiesel for diesel, which is all consumed in different cropping stages. Data were collected by direct field observation methods, and questionnaires applied to Brazilian facilities. Three sugarcane mills situated in Sao Paulo State and one palm oil refinery located in Para State were surveyed. The information was supplemented by secondary sources. Results demonstrated that fossil fuel use and greenhouse gas emissions decreased, whereas energy efficiency increased when JSEB was compared to TSES. In comparison with TSES, the energy balance of JSEB was 1.7 greater. In addition, JSEB released 23% fewer GHG emissions than TSES. The ecosystem carbon payback time for Cerrado, Cerradao, and Degraded Grassland of JSEB was respectively 4, 7.7 and -7.6 years. These are typical land use types of the Brazilian Cerrado region for which JSEB was conceived. (C) 2012 Elsevier Ltd. All rights reserved.
Resumo:
The liquid-liquid equilibria of systems composed of rice bran oil, free fatty acids, ethanol and water were investigated at temperatures ranging from 10 to 60 degrees C. The results of the present study indicated that the mutual solubility of the compounds decreased with an increase in the water content of the solvent and a decrease in the temperature of the solution. The experimental data set was correlated by applying the UNIQUAC model. The average variance between the experimental and calculated compositions was 0.35%, indicating that the model can accurately predict behavior of the compounds at different temperatures and degrees of hydration. The adjustment of interaction parameters enables both the simulation of liquid-liquid extractors for deacidification of vegetable oil and the prediction of phase compositions for the oil and alcohol-rich phases that are generated during cooling of the stream exiting the extractor (when using ethanol as the solvent). (C) 2012 Elsevier Ltd. All rights reserved.
Resumo:
Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.
Resumo:
The pyrolysis of a sludge produced in the waste water treatment plant of an oil refinery was studied in a pilot plant reactor provided with a system for condensation of semivolatile matter. The study comprises experiments at 350, 400, 470 and 530 °C in nitrogen atmosphere. Analysis of all the products obtained (gases, liquids and chars) are presented, with a thermogravimetric study of the char produced and analysis of main components of the liquid. In the temperature range studied, the composition of the gas fraction does not appreciably vary. In the liquids, the light hidrocarbon yield increases with increasing temperature, whereas the aromatic compounds diminish. The decomposition of the solid fraction has been analysed, finding a material that reacts rapidly with oxygen regardless of the conditions it is formed.
Resumo:
Edible oil is an important contaminant in water and wastewater. Oil droplets smaller than 40 μm may remain in effluent as an emulsion and combine with other contaminants in water. Coagulation/flocculation processes are used to remove oil droplets from water and wastewater. By adding a polymer at proper dose, small oil droplets can be flocculated and separated from water. The purpose of this study was to characterize and analyze the morphology of flocs and floc formation in edible oil-water emulsions by using microscopic image analysis techniques. The fractal dimension, concentration of polymer, effect of pH and temperature are investigated and analyzed to develop a fractal model of the flocs. Three types of edible oil (corn, olive, and sunflower oil) at concentrations of 600 ppm (by volume) were used to determine the optimum polymer dosage and effect of pH and temperature. To find the optimum polymer dose, polymer was added to the oil-water emulsions at concentration of 0.5, 1.0, 1.5, 2.0, 3.0 and 3.5 ppm (by volume). The clearest supernatants obtained from flocculation of corn, olive, and sunflower oil were achieved at polymer dosage of 3.0 ppm producing turbidities of 4.52, 12.90, and 13.10 NTU, respectively. This concentration of polymer was subsequently used to study the effect of pH and temperature on flocculation. The effect of pH was studied at pH 5, 7, 9, and 11 at 30°C. Microscopic image analysis was used to investigate the morphology of flocs in terms of fractal dimension, radius of oil droplets trapped in floc, floc size, and histograms of oil droplet distribution. Fractal dimension indicates the density of oil droplets captured in flocs. By comparison of fractal dimensions, pH was found to be one of the most important factors controlling droplet flocculation. Neutral pH or pH 7 showed the highest degree of flocculation, while acidic (pH 5) and basic pH (pH 9 and pH 11) showed low efficiency of flocculation. The fractal dimensions achieved from flocculation of corn, olive, and sunflower oil at pH 7 and temperature 30°C were 1.2763, 1.3592, and 1.4413, respectively. The effect of temperature was explored at temperatures 20°, 30°, and 40°C and pH 7. The results of flocculation of oil at pH 7 and different temperatures revealed that temperature significantly affected flocculation. The fractal dimension of flocs formed in corn, olive and sunflower oil emulsion at pH 7 and temperature 20°, 30°, and 40°C were 1.82, 1.28, 1.29, 1.62, 1.36, 1.42, 1.36, 1.44, and 1.28, respectively. After comparison of fractal dimension, radius of oil droplets captured, and floc length in each oil type, the optimal flocculation temperature was determined to be 30°C. ^
Resumo:
This thesis deals with the response of biodegradation of selected anthropogenic organic contaminants and natural autochthonous organic matter to low temperature in boreal surface soils. Furthermore, the thesis describes activity, diversity and population size of autotrophic ammonia-oxidizing bacteria (AOB) in a boreal soil used for landfarming of oil-refinery wastes, and presents a new approach, in which the particular AOB were enriched and cultivated in situ from the landfarming soil onto cation exchange membranes. This thesis demonstrates that rhizosphere fraction of natural forest humus soil and agricultural clay loam soil from Helsinki Metropolitan area were capable of degrading of low to moderate concentrations (0.2 50 µg cm-3) of PCP, phenanthrene and 2,4,5-TCP at temperatures realistic to boreal climate (-2.5 to +15 °C). At the low temperatures, the biodegradation of PCP, phenanthrene and 2,4,5-TCP was more effective (Q10-values from 1.6 to 7.6) in the rhizosphere fraction of the forest soil than in the agricultural soil. Q10-values of endogenous soil respiration (carbon dioxide evolution) and selected hydrolytic enzyme activities (acetate-esterase, butyrate-esterase and β-glucosidase) in acid coniferous forest soil were 1.6 to 2.8 at temperatures from -3 to +30 °C. The results indicated that the temperature dependence of decomposition of natural autochthonous soil organic matter in the studied coniferous forest was only moderate. The numbers of AOB in the landfarming (sandy clay loam) soil were determined with quantitative polymerase chain reaction (real-time PCR) and with Most Probable Number (MPN) methods, and potential ammonium oxidation activity was measured with the chlorate inhibition technique. The results indicated presence of large and active AOB populations in the heavily oil-contaminated and urea-fertilised landfarming soil. Assessment of the populations of AOB with denaturing gradient gel electrophoresis (DGGE) profiling and sequence analysis of PCR-amplified 16S rRNA genes showed that Nitrosospira-like AOB in clusters 2 and 3 were predominant in the oily landfarming soil. This observation was supported by fluorescence in situ hybridization (FISH) analysis of the AOB grown on the soil-incubated cation-exchange membranes. The results of this thesis expand the suggested importance of Nitrosospira-like AOB in terrestrial environments to include chronically oil-contaminated soils.
Resumo:
Heat exchanger design is a complex task involving the selection of a large number of interdependent design parameters. There are no established general techniques for optimizing the design, though a few earlier attempts provide computer software based on gradient methods, case study methods, etc. The authors felt that it would be useful to determine the nature of the optimal and near-optimal feasible designs to devise an optimization technique. Therefore, in this article they have obtained a large number of feasible designs of shell and tube heat exchangers, intended to perform a given heat duty, by an exhaustive search method. They have studied how their capital and operating costs varied. The study reveals several interesting aspects of the dependence of capital and total costs on various design parameters. The authors considered a typical shell and tube heat exchanger used in an oil refinery. Its heat duty, inlet temperature and other details are given.
Resumo:
Introdução: o óxido nítrico (NO) é um gás inorgânico com uma meia-vida curta e tem um papel crítico na manutenção da homeostase vascular e fluidez sanguínea. O NO é sintetizado a partir do aminoácido L-arginina por uma família de enzimas NO sintases (NOS). Estudos têm mostrado que eritrócitos expressam NOS endotelial (eNOS) funcional, que serve como uma fonte de NO intraluminal. Além disso, eritrócitos participam da defesa antioxidante removendo os radicais livres e prevenindo o dano oxidativo às membranas biológicas e a destruição do NO. Dietas hiperlípidicas estão associadas a um risco aumentado de doença cardiovacular e síndrome metabólica, mas os exatos mecanismos não estão completamente esclarecidos. O objetivo deste estudo foi investigar os efeitos de diferentes dietas hiperlípidicas na via L-arginina-NO e o estresse oxidativo em eritrócitos de camundongos. Metodologia: camundongos machos C57BL/6 de três meses de idade receberam diferentes dietas por 10 semanas: dieta normolipídica ou dieta hiperlipídica contendo banha de porco (HB), óleo de oliva (HO), óleo de girassol (HG) ou óleo de canola (HC). Foram analisados o transporte de L-arginina mediado pelos transportadores catiônicos y+ e y+L, a atividade da NOS, a expressão da eNOS e da NOS induzível (iNOS), a formação de substâncias reativas ao ácido tiobarbitúrico (TBARS) e a atividade das enzimas antioxidantes catalase (CAT) e superóxido dismutase (SOD). Resultados: o transporte total de L-arginina estava aumentado no grupo HO em comparação aos controles e aos outros grupos com dieta hiperlipídica. Quando o transporte foi fracionado, o sistema y+ estava mais ativado no grupo HO em relação aos controles e outros grupos que receberam dieta hiperlipídica. O transporte de L-arginina via sistema y+L estava maior nos grupos HO, HG e HC comparados aos grupos controle e HB. Adicionalmente, a atividade basal da NOS e a expressão de eNOS estavam aumentadas em eritrócitos independente do tipo de dieta hiperlípidica insaturada. Observou-se uma maior expressão da iNOS no grupo HO comparado ao controle. Em contraste, o grupo HB apresentou uma inibição da via L-arginina-NO. A análise da peroxidação lipídica, através da formação de TBARS, e da atividade da enzima antioxidante CAT não revelou diferenças entre os grupos, ao contrário do grupo HO, que induziu uma ativação de outra enzima antioxidante, a SOD. Conclusões: o presente estudo proporciona a primeira evidência de que os sistemas y+ e y+L regulam o transporte aumentado de L-arginina em eritrócitos de camundongos do grupo HO. Além disso, todas as dietas hiperlipídicas insaturadas induzem um aumento da atividade basal da NOS associada a uma expressão elevada da eNOS. É possível que diferentes mudanças na composição lipídica da membrana plasmática induzidas pelas dietas possam afetar transportadores e enzimas nos eritrócitos. Além disso, a inibição da via L-arginina-NO no grupo HB pode contribuir para o desenvolvimento da aterosclerose, enquanto dietas hiperlipídicas insaturadas podem ter um efeito protetor via aumento da geração de NO.
Resumo:
Ácidos graxos são moléculas bioativas endógenas e exógenas, que podem ser potentes mediadores e/ou reguladores de muitos processos celulares, no entanto, os seus efeitos no reparo de lesões cutâneas não estão bem esclarecidos. O objetivo deste trabalho foi investigar os efeitos da suplementação com diferentes óleos comestíveis na cicatrização de lesões cutâneas. Para isso, ratos Wistar machos (6-8 semanas/ 150200g) foram separados em quatro grupos: Um grupo controle (n=7) e três grupos experimentais (n=21). Trinta dias antes de realizarmos a lesão no dorso de cada animal, demos início a suplementação diária pelo método de gavagem com 1,5ml/kg de óleo de girassol, linhaça ou peixe e esta se manteve até o dia da eutanásia (d14). Em d0 uma lesão excional (1cm) foi realizada na parte dorsal de cada animal. A contração da lesão e re-epitelização foram medidas em d0, d7 e d14. Ao sacrificarmos os animais a lesão foi coletada juntamente com pele normal adjacente. O fechamento da lesão foi significativamente maior no grupo de controle (área lesada 582%) em d7, quando comparado com os outros grupos (grupo girassol 682%, linhaça 772% e peixe 732%) com p<0,05, para todos. Em d14 observamos menor área lesada no grupo controle (área lesada 211%) em relação aos grupos suplementados com óleo de linhaça e peixe (área lesada dos grupos linhaça 271% e peixe 271%), com p<0,05 para ambos os grupos. Não observamos diferença no fechamento da lesão quando comparamos os grupos controle (área lesada 211%) e girassol (área lesada 251%). Em relação ao infiltrado inflamatório observamos uma quantidade moderada nos grupos controle, linhaça e peixe, enquanto que no grupo girassol foram encontradas poucas células inflamatórias. Grande número de miofibroblastos foi observado nos grupos controle e girassol na região superficial do tecido de granulação. Entretanto, nos grupos linhaça e peixe observamos poucos miofibroblastos e muitos vasos sanguíneos dilatados. Os grupos controle e girassol apresentaram vasos sanguíneos ocluídos e concentrados na região profunda do tecido de granulação. Os grupos controle e girassol apresentaram densidade moderada de fibras colágenas na região profunda do tecido de granulação. Esse resultado foi confirmado através da dosagem de hidroxiprolina. Os níveis de hidroxiprolina estavam menores nos grupos controle e girassol quando comparados com os grupos linhaça e peixe. A suplementação com diferentes tipos de óleos comestíveis retarda o processo de contração da lesão e afeta o infiltrado inflamatório e a deposição de fibras colágenas
Resumo:
O presente estudo visa analisar os processos de transformações econômicos, políticos e socioambientais decorrentes da instalação dos grandes empreendimentos em territórios tradicionais da pesca, mais especificamente, as experiências da comunidade pesqueira da Ilha da Madeira/baía de Sepetiba/Itaguaí-RJ, desde a instalação da Cia Ingá Mercantil (1964) até os dias atuais, identificando, nos vários ciclos de industrialização: os fatores endógenos e exógenos que contribuem para a vulnerabilidade ou sustentabilidade da pesca artesanal e do meio ambiente. Sinalizando, nesta experiência, alguns aspectos que possam servir de referência para outras comunidades pesqueiras que vivenciam problemas similares. Introduzimos a problemática a partir da contextualização da pesca artesanal no Brasil, as políticas, a regulamentação da atividade, a organização dos pescadores. Ao evidenciar a pesca artesanal no estado do Rio de Janeiro, destacamos os conflitos socioambientais decorrentes da instalação de complexos industriais em territórios tradicionalmente ocupados por pescadores, com destaque para os conflitos relativos à instalação do Porto de Açu, em São João da Barra/RJ e os gasodutos para a refinaria de petróleo na baía de Guanabara. Aprofundamos a temática, a partir de um estudo de caso na Ilha da Madeira, baía de Sepetiba, Itaguaí/RJ. Esse território, tradicionalmente ocupado por pescadores, mergulhou em uma crise socioambiental a partir da década de 60 e, desde então, vem passando por diversas transformações: alteração radical da paisagem, degradação ambiental além do sufocamento da atividade pesqueira. Os fatos são evidenciados por meio de pesquisas bibliográficas, documentais, registros fotográficos, sobretudo, história de oral. Em entrevistas com informantes-chave resgatamos as memórias pessoais e, nesse percurso, fomos recuperando parte da história do território. Caracterizando a paisagem, a vida e trabalho dos pescadores, a cultura local: tradições, costumes, valores, aspectos materiais e simbólicos, em um período anterior a chegada das indústrias, quando a Ilha da Madeira era de fato, uma Ilha. Em suas narrativas os entrevistados foram pontuando as sucessões dos trágicos acontecimentos que ocorreram após a instalação da Ingá até os dias atuais. Esses fatos são demarcados em ciclos que compõem a crise socioambiental no território. Um estudo que retrata a injustiça ambiental, a vulnerabilidade de uma comunidade pesqueira, cuja experiência serve de alerta para outras comunidades tradicionais. Ressaltamos a importância das articulações entre os movimentos locais com instâncias extras locais, sinalizando para a necessidade de democratização dos processos decisórios e da gestão compartilhada dos recursos de uso comum. Também pontuamos a urgência de superação do paradigma que dissocia desenvolvimento, natureza e sociedade, fortalecendo uma lógica de produção que, ao se impor como hegemônica sufoca todas outras formas de organização do trabalho.