876 resultados para Fruit removal


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Source point treatment of effluents with a high load of pharmaceutical active compounds (PhACs), such as hospital wastewater, is a matter of discussion among the scientific community. Fungal treatments have been reported to be successful in degrading this type of pollutants and, therefore, the white-rot fungus Trametes versicolor was applied for the removal of PhACs from veterinary hospital wastewater. Sixty-six percent removal was achieved in a non-sterile batch bioreactor inoculated with T. versicolor pellets. On the other hand, the study of microbial communities by means of DGGE and phylogenetic analyses led us to identify some microbial interactions and helped us moving to a continuous process. PhAC removal efficiency achieved in the fungal treatment operated in non-sterile continuous mode was 44 % after adjusting the C/N ratio with respect to the previously calculated one for sterile treatments. Fungal and bacterial communities in the continuous bioreactors were monitored as well.

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The aim of this study was to evaluate tetracycline antibiotic (TA) removal from contaminated water by Moringa oleifera seed preparations. The composition of synthetic water approximate river natural contaminated water and TA simulated its presence as an emerging pollutant. Interactions between TA and protein preparations (extract; fraction and lectin) were also evaluated. TA was determined by solid phase extraction followed by high performance liquid chromatography - mass spectrometry. Moringa extract and flour removed TA from water. Extract removed TA in all concentrations and better removal (40%) was obtained with 40 mg L1; seed flour (particles < 5mm), 1.25 g L1 and 2.50 g L1 removed 28 and 29% of tetracycline, respectively; particles > 5 mm (0.50 g L1) removed 55% of antibiotic. Interactions between TA and seed preparations were assayed by haemagglutinating activity (HA). Specific HA (SHA) of extract (pH 7) was abolished with tetracycline (5 mg L1); fraction (75%) and lectin HA (97%) were inhibited with TA. Extract SHA decreased by 75% at pH 8. Zeta potential (ZP) of extract 700 mg L1 and tetracycline 50 mg L1 , pH range 5 to 8, showed different results. Extract ZP was more negative (10.73 mV to 16.00 mV) than tetracycline ZP (0.27 mV to 20.15 mV); ZP difference was greater in pH 8. The focus of this study was achieved since moringa preparations removed TA from water and compounds interacting with tetracycline involved at least lectin binding sites. This is a natural process, which do not promote environmental damage.

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Zearalenone (ZEN) is a mycotoxin that has relatively low acute toxicity. However, it is a potent oestrogen, interfering with the reproductive tract of animals. Among other effects, ZEN decreases animals fertility, and induces fibrosis in the uterus, breast cancer and endometrial carcinoma (Zinedine et al., 2007). Anti-mycotoxin additives (AMA) are defined as a group of products that, when added to animal feed, are capable of adsorbing, inactivating, or neutralizing mycotoxins in the gastrointestinal tract of animals. One example of these products are adsorbents based on yeast cell walls, a safe and beneficial animal feed additive (Abreu et al., 2008). When based on active cells, yeast based products also act as a probiotic, contributing to improve the general animal health because it stimulates their immune system and promotes the integrity of intestinal mucosa (Albino et al., 2006). Strains of Saccharomyces cerevisiae isolated from silage were tested for their ZEN removal capability. Their effect on - and b-zearalenol (-ZOL and b-ZOL) was also tested. Strains were grown on YPD separately supplemented with ZEN, -ZOL and b-ZOL, and their elimination from culture media was quantified over time by HPLC-FL.

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Mycotoxins are toxic secondary metabolites produced by certain moulds, being ochratoxin A (OTA) one of the most relevant. Its chemical structure is a dihydro-isocoumarin connected at the 7-carboxy group to a molecule of L--phenylalanine via an amide bond. OTA contamination of wines might be a risk to consumer health, thus requiring treatments to achieve acceptable standards for human consumption [1]. According to the Regulation No. 1881/2006 of the European Commission, the maximum limit for OTA in wine is 2 µg/kg [2]. Therefore, the aim of this work was to know the effect of different fining agents on OTA removal, as well as their impact on white and red wine physicochemical characteristics. To evaluate their efficiency, 11 commercial fining agents (mineral, synthetic, animal and vegetable proteins) were used to get new approaches on OTA removal from white and red wines. Trials were performed in wines artificially supplemented (at a final concentration of 10 µg/L) with OTA. The most effective fining agent in removing OTA (80%) from white wine was a commercial formulation that contains gelatine, bentonite and activated carbon. Removals between 10-30% were obtained with potassium caseinate, yeast cell walls and pea protein. With bentonites, carboxymethylcellulose, polyvinylpolypyrrolidone and chitosan no considerable OTA removal was verified. In red wine, removals between 6-19% were obtained with egg albumin, yeast cell walls, pea protein, isinglass, gelatine, polyvinylpolypyrrolidone and chitosan. The most effective fining agents in removing OTA from red wine were an activated carbon (66%) followed again by the commercial formulation (55%), being activated carbon a well-known adsorbent of mycotoxins. These results may provide useful information for winemakers, namely for the selection of the most appropriate oenological product for OTA removal, reducing wine toxicity and simultaneously enhancing food safety and wine quality.

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The presence of mycotoxins in foodstuff is a matter of concern for food safety. Mycotoxins are toxic secondary metabolites produced by certain molds, being ochratoxin A (OTA) one of the most relevant. Wines can also be contaminated with these toxicants. Several authors have demonstrated the presence of mycotoxins in wine, especially ochratoxin A (OTA) [1]. Its chemical structure is a dihydro-isocoumarin connected at the 7-carboxy group to a molecule of L--phenylalanine via an amide bond. As these toxicants can never be completely removed from the food chain, many countries have defined levels in food in order to attend health concerns. OTA contamination of wines might be a risk to consumer health, thus requiring treatments to achieve acceptable standards for human consumption [2]. The maximum acceptable level of OTA in wines is 2.0 g/kg according to the Commission regulation No. 1881/2006 [3]. Therefore, the aim of this work was to reduce OTA to safer levels using different fining agents, as well as their impact on white wine physicochemical characteristics. To evaluate their efficiency, 11 commercial fining agents (mineral, synthetic, animal and vegetable proteins) were used to get new approaches on OTA removal from white wine. Trials (including a control without addition of a fining agent) were performed in white wine artificially supplemented with OTA (10 µg/L). OTA analysis were performed after wine fining. Wine was centrifuged at 4000 rpm for 10 min and 1 mL of the supernatant was collected and added of an equal volume of acetonitrile/methanol/acetic acid (78:20:2 v/v/v). Also, the solid fractions obtained after fining, were centrifuged (4000 rpm, 15 min), the resulting supernatant discarded, and the pellet extracted with 1 mL of the above solution and 1 mL of H2O. OTA analysis was performed by HPLC with fluorescence detection according to Abrunhosa and Venâncio [4]. The most effective fining agent in removing OTA (80%) from white wine was a commercial formulation that contains gelatine, bentonite and activated carbon. Removals between 10-30% were obtained with potassium caseinate, yeast cell walls and pea protein. With bentonites, carboxymethylcellulose, polyvinylpolypyrrolidone and chitosan no considerable OTA removal was verified. Following, the effectiveness of seven commercial activated carbons was also evaluated and compared with the commercial formulation that contains gelatine, bentonite and activated carbon. The different activated carbons were applied at the concentration recommended by the manufacturer in order to evaluate their efficiency in reducing OTA levels. Trial and OTA analysis were performed as explained previously. The results showed that in white wine all activated carbons except one reduced 100% of OTA. The commercial formulation that contains gelatine, bentonite and activated carbon (C8) reduced only 73% of OTA concentration. These results may provide useful information for winemakers, namely for the selection of the most appropriate oenological product for OTA removal, reducing wine toxicity and simultaneously enhancing food safety and wine quality.

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Supplementary data associated with this article can be found, in the online version, at: http://dx.doi.org/10.1016/j.cej.2016.03.148.

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Natural mineral waters (still), effervescent natural mineral waters (sparkling) and aromatized waters with fruit-flavors (still or sparkling) are an emerging market. In this work, the capability of a potentiometric electronic tongue, comprised with lipid polymeric membranes, to quantitatively estimate routinely quality physicochemical parameters (pH and conductivity) as well as to qualitatively classify water samples according to the type of water was evaluated. The study showed that a linear discriminant model, based on 21 sensors selected by the simulated annealing algorithm, could correctly classify 100 % of the water samples (leave-one out cross-validation). This potential was further demonstrated by applying a repeated K-fold cross-validation (guaranteeing that at least 15 % of independent samples were only used for internal-validation) for which 96 % of correct classifications were attained. The satisfactory recognition performance of the E-tongue could be attributed to the pH, conductivity, sugars and organic acids contents of the studied waters, which turned out in significant differences of sweetness perception indexes and total acid flavor. Moreover, the E-tongue combined with multivariate linear regression models, based on sub-sets of sensors selected by the simulated annealing algorithm, could accurately estimate waters pH (25 sensors: R 2 equal to 0.99 and 0.97 for leave-one-out or repeated K-folds cross-validation) and conductivity (23 sensors: R 2 equal to 0.997 and 0.99 for leave-one-out or repeated K-folds cross-validation). So, the overall satisfactory results achieved, allow envisaging a potential future application of electronic tongue devices for bottled water analysis and classification.

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Los sistemas de agua dulce constituyen fuentes vitales para el desarrollo de la vida. Entre otras causas, el excesivo y poco controlado uso de pesticidas por las prácticas agrícolas modernas ha contribuido con la degradación de estos ecosistemas en la provincia de Córdoba (Secretaría de Ambiente, 2008). Los pesticidas son compuestos tóxicos y químicamente estables en el ambiente. Diversas especies microbianas presentan la capacidad para mineralizar dichos compuestos, siendo uno de los mecanismos de descomposición más importante. En el presente trabajo se pretende (1) Detectar y cuantificar principios activos de pesticidas en diferentes aguas ambientales de la región centro-sur de la provincia de Córdoba; (2) Aislar y caracterizar especies bacterianas a partir de muestras de aguas superficiales y subterráneas de la región que demuestren ser eficientes en la biodegradación de diferentes pesticidas. Para ello, se estudiará la presencia de 10 pesticidas organoclorados y organofosforados (lindano, 2,4D, DDT, p,p-DDE, �-endosulfán, �-endosulfán, clorpirifós, dimetoato) y herbicidas (atrazina) en muestras de agua superficiales y subterráneas (8 - 12m de profundidad) de la región agrícola centro-sur de Córdoba. Se establecerán diferentes puntos de muestreo en las principales cuencas hidrográficas: Río Tercero y Embalse de Río Tercero, Canal Desviador de Bell Ville, Laguna La Salada, Río Saladillo, Río Carcarañá y Río Cuarto. La determinación de pesticidas se realizará mediante Cromatografía de Gases (GC). Conjuntamente, se realizará el aislamiento de microorganismos a partir de las muestras de agua suplementadas con diferentes concentraciones de pesticidas (López et al., 2005) y se procederá a la caracterización morfológica y bioquímica (Lechevalier, 1989). Se realizarán curvas de crecimiento (DO600) y se determinará la viabilidad celular mediante el método de recuento en placa. El potencial catabólico de cada aislamiento se determinará analizando la concentración residual de pesticidas en el sobrenadante de los cultivos (Benimeli et al, 2003) y mediante ensayos de resting-cell (Hernández et al, 2008). Finalmente se realizará la caracterización genética (Weisburg, 1991) de los aislamientos que demuestren una mayor eficiencia en la biodegradación de pesticidas. El presente estudio pretende abordar una temática prioritaria como es la contaminación ambiental de ecosistemas acuáticos de la provincia de Córdoba. la detección de principios activos de pesticidas sería, por lo tanto, un indicador de contaminación de origen antropológica y brindaría información respecto al deterioro de la calidad del agua. Por otra parte, el aislamiento de bacterias adaptadas a las condiciones ecológicas de la región y capaces de metabolizar eficientemente diferentes pesticidas como fuentes de carbono y energía sería beneficioso para su utilización en futuros ensayos de biorremediación.

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Este proyecto estudiará las estrategias de vida implementadas por familias productoras fruti hortícolas que viven en Colonia Tirolesa y Chacra de la Merced, lugares que forman parte del cinturón verde de la Ciudad de Córdoba; y su relación con los procesos de diferenciación social, asociados a cambios productivos, económicos, culturales y sociales que están condicionados por el modelo de expansión capitalista. A partir del análisis del capital económico, social, cultural y simbólico se identificará en un contexto rural las motivaciones, logicas productivas y conocimientos agrícolas que incidieron en las decisiones asumidas ante problematicas emergentes, tales como limitaciones para adquirir nuevos paquetes tecnológicos, el impacto ambiental causados por la no conservación y sustentabilidad de los recursos y las consecuencias sociales vinculadas a los laxos de familia, el trabajo y la calidad de vida.Se plantean las siguientes hipótesis: 1)Algunas familias productoras implementaron estrategias de vida que se relacionan con criterios de autosustentabilidad, conocimientos agrícolas tradicionales y pautas culturales.2) Los nuevos espacios productivos no son compatibles con agroecosistemas sustentables. 3) Las nuevas tecnologías causaron impactos en la actividad productiva e incidieron en la economía, calidad de vida y vinculos familiares. 4)El modo de producción familiar fue reemplazado por el modo de producción capitalista lo que incidió en la producción agrícola y en la conservación de los recursos.El objetivo principal es descubrir las estrategias de vida implementadas por un grupo de familias, trabajadoras fruti hortícolas, en respuesta a las transformaciones productivas, tecnológicas y socio económicas impuestas por el modelo de acumulación vigente.Para ello se caracterizará los ambitos productivos de trabajo a campo, identificando la disponibilidad de capital y los conocimientos técnicos y de manejo. También se analizarán las pautas y valores culturales, el impacto de las nuevas tecnologías y la incidencia social, vinculada a los cambios en los modos de producción.El abordaje será de tipo cualitativo, recavando información para elaborar una descripción detallada de las estrategias de vida adoptadas a partir de la década de los noventa. Se tomará como unidad de análisis a las familias que trabajaron o trabajan en la producción de hortalizas o frutales. Se realizarán combinaciones entre procedimientos Tipológicos a Priori; Históricos Comparativos y casos Unitarios. Se analizará las normativas vigentes en relación al uso y calidad del agua y del suelo; también imágenes satelitales para analizar los procesos de cambio en el uso del territorio y del recurso suelo. Se pretende realizar un aporte relacionado con el conocimiento de: la sustentabilidad de los sistemas productivos, la pobreza y los modos de vida de los productores fruti hortícolas que persistencia en ambientes degradados; en una franja intermedia entre el campo y la ciudad.

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Magdeburg, Univ., Fak. für Informatik, Diss., 2013

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A localização do superfosfato (marcado com P32) no maracujá em produção foi estudada em condições de plantação comercial. Verificou-se que as aplicações em sulcos circulares ou faixas superficiais ao redor da planta tem eficiência equivalente sendo esses métodos três vezes superiores à localização do adubo em furos no solo. A pulverização foliar, por sua vez, mostrou-se 20 vezes mais eficiente que a aplicação no solo de acordo com os dois primeiros métodos.

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1. Tagged superphosphate was applied to 2.5 year old passion fruit plants from a commercial plantation established in a sandy loam. 2. 100 grams of the fertilizer were distributed in the following ways: in a circular furrow 20 cm around the plant 40 cm from the stems; in a circular strip 10 cm wide, 40 cm from the stems; in six holes around the plants, 40 cm from the stems 20 cm deep, 2.5 cm in diameter. 3. 10 grams of the fertilizer in 11 of water were sprayed to the leaves. 4. Three weeks after the treatments were made, leaf samples were taken for analysis. 5. Determinations of specific activities both in the leaves and in the fertilizer used have shown that R in the plant was derived from the superphosphate in the following relative proportions (by making the first treatment equal to 100): circular furrow = 100; circular strip = 120; holes = 30; foliar spray = 230.

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Fruitone CPA was applied on the two terminals hands of the banana bunch, using the following doses: 0-159-300 and 600 ppm. Fruitone did not affect fruit weightm but increased fruit lenght. This alteration was greater with Fruitone at 600 ppm.

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v.31:no.16(1947)