953 resultados para COMPETITIVE HEAVY METALS ADSORPTION


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O chumbo é um importante poluente ambiental. A levedura Saccharomyces cerevisiae constitui um modelo útil para o estudo dos efeitos tóxicos do chumbo. O conhecimento dos mecanismos de defesa e resistência à presença de metais pesados poderá ser útil em tecnologias de proteção ambiental, nomeadamente no desenvolvimento de novas metodologias para a biorremediação de metais pesados. O presente trabalho teve como objetivo avaliar o impacto do Pb na capacidade proliferativa, na integridade membranar e na produção intracelular de espécies reativas de oxigénio (ROS), na estirpe laboratorial da levedura Saccharomyces cerevisiae BY4741 (estirpe selvagem, WT). Foi também estudado o papel das mitocôndrias, como fonte de ROS induzida por Pb, e o envolvimento da H+-ATPase vacuolar (V-ATPase) e de transportadores vacuolares pertencentes à superfamília ABC (de ATP-binding cassette) na defesa contra a toxicidade do Pb. O estudo cinético do impacto de duas concentrações de Pb na viabilidade das leveduras (avaliado através de um ensaio clonogénico), na integridade da membrana celular (determinada com iodeto de propídio) e na produção intracelular de ROS (o anião superóxido foi detetado com dihidroetídio e o peróxido de hidrogénio com 2’,7’- diclorodihidrofluoresceína), revelou uma perda progressiva da capacidade proliferativa (53 e 17% de células viáveis, após a exposição durante 3h a 250 ou 1000 µmol/l de chumbo, respetivamente), coincidente com a acumulação intracelular de anião superóxido e de peróxido de hidrogénio, na ausência de perda da integridade membranar. A importância das mitocôndrias na produção de ROS, induzida por chumbo, foi levada a cabo usando um mutante deficiente respiratório desprovido de ADN mitocondrial (ƿ0). Quando comparado com a respetiva estirpe parental, o mutante ƿ0 apresentou uma maior resistência ao Pb e uma menor produção de ROS induzida por Pb. A exposição das células da estirpe BY4741 a 250 e 1000 µmol/l de chumbo originou a formação de 49 e 58% de células deficientes respiratórias, respetivamente. A função da V-ATPase, na desintoxicação de chumbo, foi avaliada utilizando mutantes com uma estrutura vacuolar normal mas defetivos em subunidades da VATPase (vma1Δ, vma2Δ, vma3Δ e vph1Δ). Comparativamente às células da estirpe WT, todos os mutantes testados, sem V-ATPase funcional, apresentaram uma maior suscetibilidade ao Pb. O papel dos transportadores vacuolares pertencentes à superfamília ABC, na defesa contra a toxicidade induzida por chumbo, foi levada a cabo utilizando mutantes sem os transportadores Ycf1p ou Vmr1p. Os resultados preliminares mostraram que quando comparadas com as células da estirpe WT, as células das estirpes ycf1Δ ou vmr1Δ não apresentavam uma maior perda da viabilidade. A modificação da morfologia vacuolar, em células expostas a chumbo, foi visualizada utilizando a estirpe Vma2p-GFP. O tratamento das células com Pb originou a fusão dos vacúolos de tamanho médio num único vacúolo de grande dimensão. Em conclusão, os estudos desenvolvidos no presente trabalho, utilizando a estirpe laboratorial BY4741, mostraram que a perda da capacidade proliferativa das leveduras, induzida pelo chumbo, pode ser atribuída à acumulação intracelular do anião superóxido e de peróxido de hidrogénio. As mitocôndrias parecem ser uma das principais fontes de ROS induzido por Pb e, simultaneamente, um dos principais alvos da sua toxicidade. Em S. cerevisiae, o vacúolo desempenha um papel importante na desintoxicação do Pb. A modificação da morfologia vacuolar após exposição ao chumbo poderá ser a consequência da acumulação de Pb no vacúolo. Enquanto os transportadores da superfamília ABC parecem não estar envolvidos na sequestração vacuolar de Pb, é necessária a presença, num estado funcional, da V-ATPase para que ocorra a compartimentação do Pb. Muito provavelmente, a compartimentação do Pb no vacúolo previne a sua acumulação no citosol e o desencadear dos respetivos efeitos tóxicos.

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Dissertação para obtenção do Grau de Mestre em Engenharia do ambiente, perfil de engenharia sanitária

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Thesis submitted to obtain the Doctoral degree in Energy and Bioenergy

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Dissertação para obtenção do Grau de Mestre em Engenharia do Ambiente Perfil de Engenharia de Sistemas Ambientais

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Dissertação para obtenção do Grau de Mestre em Engenharia do Ambiente, Perfil de Engenharia Sanitária

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Phosphorus (P) is becoming a scarce element due to the decreasing availability of primary sources. Therefore, recover P from secondary sources, e.g. waste streams, have become extremely important. Sewage sludge ash (SSA) is a reliable secondary source of P. The use of SSAs as a direct fertilizer has very restricted legislation due to the presence of inorganic contaminants. Furthermore, the P present in SSAs is not in a plant-available form. The electrodialytic (ED) process is one of the methods under development to recover P and simultaneously remove heavy metals. The present work aimed to optimize the P recovery through a 2 compartment electrodialytic cell. The research was divided in three independent phases. In the first phase, ED experiments were carried out for two SSAs from different seasons, varying the duration of the ED process (2, 4, 6 and 9 days). During the ED treatment the SSA was suspended in distilled water in the anolyte, which was separated from the catholyte by a cation exchange membrane. From both ashes 90% of P was successfully extracted after 6 days of treatment. Regarding the heavy metals removal, one of the SSAs had a better removal than the other. Therefore, it was possible to conclude that SSAs from different seasons can be submitted to ED process under the same parameters. In the second phase, the two SSAs were exposed to humidity and air prior to ED, in order to carbonate them. Although this procedure was not successful, ED experiments were carried out varying the duration of the treatment (2 and 6 days) and the period of air exposure that SSAs were submitted to (7, 14 and 30 days). After 6 days of treatment and 30 days of air exposure, 90% of phosphorus was successfully extracted from both ashes. No differences were identified between carbonated and non-carbonated SSAs. Thus, SSAs that were exposed to the air and humidity, e.g. SSAs stored for 30 days in an open deposit, can be treated under the same parameters as the SSAs directly collected from the incineration process. In the third phase, ED experiments were carried out during 6 days varying the stirring time (0, 1, 2 and 4 h/day) in order to investigate if energy can be saved on the stirring process. After 6 days of treatment and 4 h/day stirring, 80% and 90% of P was successfully extracted from SSA-A and SSA-B, respectively. This value is very similar to the one obtained for 6 days of treatment stirring 24 h/day.

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There is a need to develop viable techniques for removal and recovery organic and inorganic compounds from environmental matrices, due to their ecotoxicity, regulatory obligations or potential supplies as secondary materials. In this dissertation, electro –removal and –recovery techniques were applied to five different contaminated environmental matrices aiming phosphorus (P) recovery and/or contaminants removal. In a first phase, the electrokinetic process (EK) was carried out in soils for (i) metalloids and (ii) organic contaminants (OCs) removal. In the case of As and Sb mine contaminated soil, the EK process was additionally coupled with phytotechnologies. In a second phase, the electrodialytic process (ED) was applied to wastes aiming P recovery and simultaneous removal of (iii) toxins from membrane concentrate, (iv) heavy metals from sewage sludge ash (SSA), and (v) OCs from sewage sludge (SS). EK enhanced phytoremediation showed to be viable for the remediation of soils contaminated with metalloids, as although remediation was low, it combines advantages of both technologies while allowing site management. EK also proved to be an effective remediation technology for the removal and degradation of emerging OCs from two types of soil. Aiming P recovery and contaminants removal, different ED cell set-ups were tested. For the membrane concentrates, the best P recovery was achieved in a three compartment (3c) cell, but the highest toxin removal was obtained in a two compartment (2c) cell, placing the matrix in the cathode end. In the case of SSA the best approach for simultaneous P recovery and heavy metals removal was to use a 2c-cell placing the matrix in the anode end. However, for simultaneous P recovery and OCs removal, SS should be placed in the cathode end, in a 2c-cell. Overall, the data support that the selection of the cell design should be done case-by-case.

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The innovative Horizon 2020 program sponsored by the European Union (EU) aims to promote and develop processes of waste integration in construction materials. However, several potential health hazards caused by building materials have been identified and, there-fore, there is an ongoing need to develop new recycling methods for hazardous wastes and effi-cient barriers in order to prevent toxic releases from the new construction solutions with wastes. This paper presents an overview that focus on two main aspects: the identification of the health risks related to radioactivity and heavy metals present in building materials and identification of these toxic substances in new construction solutions that contain recycled wastes. Different waste materials were selected and distinct methodologies of toxicity evaluation are presented to analyse the potential hazardous, the feasibility of using those wastes and the achievement of op-timal construction solutions involving wastes.

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Tese de Doutoramento em Biologia de Plantas

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La contaminación ambiental por metales pesados como el cromo y por compuestos orgánicos como los fenoles es un grave problema a nivel mundial debido a su toxicidad y a sus efectos adversos sobre los seres humanos, la flora y la fauna, tanto por su acumulación en la cadena alimentaria como por su continua persistencia en el medio ambiente. En un estudio preliminar, efectuado por nuestro laboratorio, se han detectado elevados niveles de estos contaminantes en sedimentos y efluentes en zonas industriales del sur de la provincia de Córdoba, lo cual plantea la necesidad de removerlos. Entre las tecnologías disponibles, la biorremediación, que se basa en el uso de sistemas biológicos, como los microorganismos, para la detoxificación y la degradación de contaminantes, se presenta como una alternativa probablemente más efectiva y de menor costo que las técnicas convencionales. Sin embargo, la aplicación de esta tecnología depende en gran parte de la influencia de las características particulares y específicas de la zona a remediar. En consecuencia, en primer lugar se caracterizará la zona de muestreo y se aislarán e identificarán microorganismos nativos de la región, tolerantes a cromo y fenol, a partir de muestras de suelo, agua y sedimentos, ya que podrían constituir una adecuada herramienta biotecnológica, mejor adaptada al sitio a tratar. Posteriormente se estudiará la biorremediación de Cr y fenol utilizando dichos microorganismos, analizando su capacidad para biotransformar, bioacumular o bioadsorber a estos contaminantes, y se determinarán las condiciones óptimas para el tratamiento. Se analizarán los posibles mecanismos fisiológicos, bioquímicos y moleculares involucrados en la remediación, que constituye una etapa crucial para el diseño de una estrategia adecuada y eficiente. Finalmente, se aplicará esta tecnología a escala reactor, como una primera aproximación al tratamiento a mayor escala. De esta manera se espera reducir los niveles de estos contaminantes y así minimizar el impacto ambiental que ellos producen en suelos y acuíferos. A futuro, la utilización de los microorganismos seleccionados, de manera individual o formando consorcios, para el tratamiento de efluentes industriales previa liberación al medio ambiente, o su uso en bioaumento, constituirían posibles alternativas de aplicación. Los principales impactos científico-tecnológicos del proyecto serán: (a) la generación de una nueva tecnología biológica de decontaminación de cromo y fenol, intentando presentar soluciones frente a una problemática ambiental que afecta a nuestra región, pero que además es común a la mayoría de los países, (b) la formación de nuevos recursos humanos en el área y (c) el trabajo en colaboración con otros grupos de investigación que se destacan en el área de biotecnología ambiental. Environmental pollution produced by heavy metals, such as chromium and organic compounds like phenolics is a serious global problem due to their toxicity, their adverse effects on human life, plants and animals, their accumulation in the food chains and also by their persistance in the environment. In a previous study performed in our laboratory, high levels of these pollutants were detected in sediments and effluents from industrial zones of the south of Cordoba Province, which determine the need to remove them. Among various technologies, bioremediation which is based on the use of biological systems, such as microorganisms, to detoxify and to degrade contaminants, is probably the most effective alternative, and it is less expensive than other conventional technologies. However, the application of this technology depends on the influence of the particular and specific characteristics of the zone to be remediate. As a consecuence, at the first time, the zone of sampling will be characterized and then, native microorganisms, tolerant to chromium and phenol, will be isolated from soils, water and sediments and identificated. These microorganisms would be an adequate biotechnological tool, more adapted to the conditions of the site to be remediate than other ones. Then, the ability of these selected microorganisms to biotransform, bioaccumulate or biosorbe chromium and phenol will be studied and the optimal conditions for the treatment will be determined. The possible physiological, biochemical and molecular mechanisms involved in bioremediation will be also analized, because this is a crucial step in the design of an adequate and efficient remediation strategy. Finally, this technology will be applied in a reactor, as an approximation to the treatment at a major scale. A reduction in the levels of these pollutants will be expected, to minimize their environmental impact on soils and aquifers.

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Two water-culture experiments were carried out to study the absorption and the translocation of radiozinc in young coffee plants as influenced by two factors, namely, concentration of heavy metals (iron, manganese, copper and molybdenum) and method of application. Inert zinc was furnished at a uniform rate of 0.05 p.p.m.; the levels of iron supply were 0, 1.0 and 10 p.p.m.; manganese was supplied in three doses 0, 0.5, and 5 p.p.m.; copper - 0, 0.02, and 0.2 p.p.m.; molybdenum - 0, 0.01 and 0.1 p.p.m. When applied to the nutrient solution the activity of the radiozinc was 0.15 microcuries per plant. In the study of the leaf absorption, the radiozinc was supplied at the level of 0.10 microcuries per plant; in this case the material was brushed either on the lower or in the upper surface or both of two pairs of mature leaves. In both experiments the absorption period was 8 weeks. The following conclusions can be drawn: 1. Among the heavy metals herein investigated the iron concentration did not affecc the uptake of the radiozinc; by raising the level of Mn, Cu and Mo ten times, the absorption dropped to 50 per cent and even more whe compared with the control plant; however, when these micronutrients were omitted from the nutrient solution an increase in the uptake of zinc was registered only in the minus - Cu treatment. The effects of high leveds of Mn, Cu and Mo probably indicate an interionic competition for a same site on a common binding substance in the cell surface. 2. The absorption of the radiozinc directly applied to the leaf surface reached levels as high as 8 times that registered when the root uptake took place. Among the three methods of application which have been tried, brushing the lower surface of the leaves proved to be the most effective; this result is easily understood since the stomatal openings of the coffee leaves are preferentially located in the lower surface. In this treatment, about 40 per cent of the activity was absorbed and around 12 per cent were translocated either to the old or to the newer organs. 3. Data herein presented suggest that leaf sprays should be preferred - rather than soil applications - to control zinc deficiency in coffee plants when growing in field conditions.

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WATER-CULTURE EXPERIMENTS. Two water-culture experiments were carried out to study the absorption and the translocation of radiozinc in young coffee plants as influenced by two factors, namely, concentration of heavy metals (iron, man ganese, copper and molybdenum) and method of application. Inert zinc was supplied at an uniform rate of 0. 05 p. p. m.; the levels of iron supply were 0, 1.0, and 10.0 p. p.m.; manganese was supplied in three doses 0, 0.5, and 5.0 p. p.m.; copper- 0, 0. 02, and 0. 2 p. p. m.; molybdenum- 0, 0. 01, and 0. 1 p. p. m. When applied to the nutrient solution the activity os the radiozinc (as zinc chloride) was 0. 15 microcuries per plant. In the study of the leaf absorption, Zn65 was supplied at the level of 0. 10 microcuries per plant; in this case the radioative material was brushed either on the lower or on the upper surface or both two pairs of mature leaves. The absorption period was 8 weeks. The radioactivity assay showed the following results: 1 - Among the heavy metals herein investigated the iron concentration did not affect the uptake of the radiozinc; by raising the level of Mn, Cu and Mo ten times, the absorption dropped to 50 per cent and even more when compared with the control plants; when, however, these micronutrients were omitted from the nutrient solution, an increase in the uptake of zinc was registered in the minus Cu treatment only. The effects of high levels of Mn, Cu and Mo probably indicate an interionic competition for a same site on a common binding substance in the cell surface. 2 - The absorption of the radiozinc directly applied to the leaf surface reached levels as high as 8 times that registered when the root uptake took place. Among the three methods of application which have been tried, brushing the lower surface of the leaves proved to be the most effective; this result is easily understood since the stomatal openings of the coffee leaves an preferentially located in the lower surface - in this treatment, about 40 per cent of the activity was absorved and around 12 per cent were translocated either to the old or to the newer organs. Chemical analyses for heavy metals, were carried out only in the plants received Zn65Cl2 in the nutrient solution; the results were as follows; 1 - Control plants had, per 1,000 gm, of dry weight the following amounts in mg.: Zn- 48 in the roots and 29 in the tops; Fe- 165 in the roots and 9 in the tops; Mn- 58 in the roots and 15 in the tops, Cu- 15 in the roots and 1. 2 in the tops; Mo- 2. 8 in the roots and 0. 45 in the tops. 2 - The effect of different levels of micronutrients in the composition of the plants can be summarized as follows: Fe and Zn- when omitted from the nutrient solution, the iron and zinc contents in the roots decreased, no variation being noted in the tops; the higher dosis caused an accumulation in the roots but no apparent effect in the tops; Mn- by omitting this micronutrient a decrease in its content in the roots was noted, where as the concentration in the tops was the same; Mo- no variation in roots and tops contents when molybdenum was omitted; higher dosis of manganese and molybdenum increased the amounts formed both in the roots and in the tops. 3 - The influence of the different concentrations of micronutrients heavy metals on the zinc content of the coffee plants can be described by saying that: Fe and Mo- no marked variation; Mn- no effect when omitted, reduced amount when the high dosis was supplied; Mn- when the plants did not receive manganese the zinc content in roots and tops was the same as in the control plants; a decrease in the zinc content of the total plant occurred when the high dosis was employed; Cu -the situation is similar to that described for manganese. Hence, results showed by the chemical analyses roughly correspond to those of the radioactivity assay; the use of the tracer technique, however, gave best informations along this line. SOIL-POTS EXPERIMENTS. The two types of soils which when selected support the most extensive coffee plantations in the State of São Paulo, Brazil: "arenito de Bauru", a light sandy soil and "terra roxa legitima", a red soil derived from basalt. Besides NPK containing salts, the coffee plants were given two doses of inert zinc (65 and 130 mg ZnCl2 per pot) and radiozinc at a total activity of 10(6) counts/minute. The results of the countings can be summarized as follows: 1 - When plants were grown in "arenito de Bauru" the activity absorbed as per cent of the total activity supplied was not affected by the dosis of inert zinc. The highest value found was around 0. 1 per cent. 2 - For the "terra roxa" plants, the situation is almost the same; there was, however, a slight increase in the absorption of the radiozinc when 130 mgm of ZnClg2 was given: a little above 0. 2 per cent of the activity supplied was absorbed. The results clearly show that the young coffee plants practically did not absorb none of the zinc supplied; two reasons at least could be pointed out to explain such a fact: 1 - Zinc fixation by an exchange with magnesium or by filling holes in the octahedral layer of aluminosilicates, probably kaolinite; 2 - No need for fertilizer zinc in the particular stage of life cycle under which the experiment was set up. The data from chemical analysis are roughly parallel to the above mentioned. When one attempts to compare - by taking data herein reported zinc uptake from nutrient solution, leaf brushing or from fertilizers in the soil, a practical conclusion can be drawn: the control of zinc deficiency in coffee plants should not be done by adding the zinc salts to the soil; in other words: the soil applications used so extensively in other countries seem not to be suitable for our conditions; hence zinc sprays should be used wherever necessary.

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La distribución de alimentos líquidos al ganado porcino es un sistema alternativo en el cual el alimento se prepara y distribuye a través de un equipo totalmente informatizado y automatizado. Además de materias primas y piensos permite también el uso de co-productos líquidos de la industria agroalimentaria o productos fermentados. Su utilización evita el coste de su transformación o eliminación permitiendo rebajar el coste de producción del cerdo porque su precio es altamente competitivo. La aplicación de alimentos líquidos fermentados tiene efectos benéficos sobre el epitelio intestinal, la microflora digestiva y el estado sanitario de los lechones, reduciendo la morbilidad y aumentando los resultados de crecimiento. Este sistema de alimentación facilita igualmente la aplicación de programas multifase ajustando diariamente el aporte a las necesidades en nutrientes del cerdo reduciendo la excreción (N, P, metales pesados) y con ello, el riesgo de contaminación medioambiental. The distribution of liquid diets for swine is an alternative system where feed is prepared and distributed by an automatic computerized device. In addition to feedstuffs and complementary dry feed, this system allows the use of fresh or fermented agri-food liquid by-products. These products are cheaper and its use as feed avoids the cost of its transformation or elimination, reducing the environmental load and the cost per kg of pig meat. The fermented liquid feed protects the intestinal epithelium, helps to control digestive microflora and animal health improving piglet growth performance after weaning. This feeding device also helps implementation of multiphase feeding programs, adjusting nutrient supplies to requirements daily, and consequently reducing the nutrient excretion (N, P, heavy metals) and the risk of environmental pollution.

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En aquest estudi s’ha determinat la deposició atmosfèrica de metalls pesants a partir dels bioindicadors Xanthoria parietina (liquen) i Hypnum cupressiforme (molsa), en 16 punts de mostreig repartits per la zona on s’ubicarà el futur parc natural de les Muntanyes de Prades (Tarragona). A partir de la comparació de les concentracions obtingudes en aquest treball amb les d’altres estudis de plantejament equiparable, es va comprovar que la majoria de valors de concentració dels metalls eren similars als d’altres zones geogràfiques estudiades, a excepció del crom i el níquel, que presentaven valors clarament més elevats. A partir de proves estadístiques (ANOVA, regressions múltiples) es va determinar que existien diferències significatives entre les concentracions de metalls dels diferents punts de mostreig. També es van detectar correlacions significatives entre les concentracions dels punts de mostreig i la distància d’aquests respecte els focus potencials de contaminació que s’havien considerat prèviament. Amb les dades obtingudes a partir un petit anàlisi de la riquesa liquènica dels punts de mostreig, es va disposar d’informació extra per poder avaluar les fonts i el patró de distribució d’aquests contaminants.

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The toxicity of heavy metals in natural waters is strongly dependent on the local chemical environment. Assessing the bioavailability of radionuclides predicts the toxic effects to aquatic biota. The technique of diffusive gradients in thin films (DGT) is largely exploited for bioavailability measurements of trace metals in waters. However, it has not been applied for plutonium speciation measurements yet. This study investigates the use of DGT technique for plutonium bioavailability measurements in chemically different environments. We used a diffusion cell to determine the diffusion coefficients (D) of plutonium in polyacrylamide (PAM) gel and found D in the range of 2.06-2.29 × 10(-6) cm(2) s(-1). It ranged between 1.10 and 2.03 × 10(-6) cm(2) s(-1) in the presence of fulvic acid and in natural waters with low DOM. In the presence of 20 ppm of humic acid of an organic-rich soil, plutonium diffusion was hindered by a factor of 5, with a diffusion coefficient of 0.50 × 10(-6) cm(2) s(-1). We also tested commercially available DGT devices with Chelex resin for plutonium bioavailability measurements in laboratory conditions and the diffusion coefficients agreed with those from the diffusion cell experiments. These findings show that the DGT methodology can be used to investigate the bioaccumulation of the labile plutonium fraction in aquatic biota.