Remediação Ambiental

A agricultura é uma das atividades mais antigas realizadas pelo Homem, sendo de grande importância para a obtenção tanto de bens alimentares como de bens para outros fins. No entanto desde o início constatou-se que as culturas eram afetadas por pragas e doenças que levavam à perda das colheitas. Este motivo deu origem à necessidade de nesses termos surgiu a aplicação de substâncias com o objetivo de proteger as colheitas. Os pesticidas são substâncias naturais ou sintéticas, aplicadas com o objetivo de proteger as plantas eliminando pragas e doenças. Para além da potencial toxicidade destas substâncias, em alguns casos a sua degradação no meio ambiente por microrganismos, hidrólise, radiação solar, etc. dá origem a produtos de degradação tanto ou mais tóxicos que os próprios pesticidas. A utilização deste tipo de substâncias acarreta problemas, visto a sua aplicação ser feita de forma a compensar perdas que ocorrem por meio de degradação, lixiviação, entre outros processos. Este tipo de aplicação leva a que haja contaminação do meio ambiente por parte dos pesticidas, pondo em risco tanto a saúde humana como os restantes seres vivos. A utilização de ciclodextrinas no encapsulamento destes compostos tem como objetivo aumentar a estabilidade do composto e promover a sua libertação de forma controlada. No presente trabalho pretende-se efetuar um estudo comparativo sobre a fotodegradação do herbicida terbutilazina e do fungicida pirimetanil livres e quando encapsulados com 2- hidroxipropil-β- ciclodextrina. De forma a quantificar os pesticidas ao longo do estudo foi utilizado o método analítico de HPLC de fase reversa. Os resultados permitiram constatar que a terbutilazina é fotoquimicamente estável, nas condições aplicadas, visto que ao fim de 75 dias de as soluções de pesticida livre em água desionizada e em água do rio apresentarem ainda 98% do pesticida inicial e as soluções de pesticida encapsulado em água desionizada e em água do rio apresentarem ainda 98% do pesticida inicial. Neste caso particular não foi possível, no intervalo de tempo considerado, avaliar a influência do encapsulamento no processo de fotodegradação da terbutilazina. Dada a baixa fotodegradação observada optou-se pela adição de peróxido de hidrogénio às soluções de controlo e 35 mM de HP-β-CD e acetona às soluções de 0 mM e 17,5 mM de HP-β-CD, para tentar promover a degradação do pesticida. Através dos resultados obtidos constatou-se que particularmente para as soluções onde foi adicionada acetona houve um aumento da velocidade de degradação no entanto esta ainda ocorria de forma lenta e muito semelhante quer para o pesticida livre quer para o encapsulado. Relativamente ao estudo da fotodegradação do pirimetanil verificou-se que ao fim de 4 dias de irradiação as soluções de pesticida livre apresentavam já alguma degradação do pesticida e tendo o período de irradiação uma duração de 53 dias foi possível para este pesticida determinar os parâmetros cinéticos em algumas das soluções. Quanto as soluções de água desionizada e água do rio com pirimetanil livre ambas apresentaram degradação do pesticida verificando-se uma cinética de reação de 1ª ordem com constantes de 0,0018 dias-1 e de 0,0060 dias-1 respetivamente. Para a solução de água desionizada com pirimetanil encapsulado não foi detetada degradação do pesticida, já para a solução com pirimetanil encapsulado em água do rio verificou-se a existência de degradação que correspondeu a uma cinética de degradação de 1ª ordem com uma constante de 0,0013 dias-1. Através dos resultados obtidos pode-se concluir que o encapsulamento do pirimetanil com 2-hidroxipropil-β-ciclodextrina é vantajoso visto diminuir a quantidade de pesticida utilizado e aumentar a eficácia do controlo das pragas.

Integration of sediment contamination with multi–biomarker responses in a novel bioindicator candidate (Sepia officinalis) for risk assessment in impacted estuaries

Dissertação para obtenção do Grau de Mestre em Engenharia do Ambiente

Determination of permethrin and its metabolites in hearts and urines of rats by GC-ECD and GC-MS

Pyrethroids are pesticides very used in agriculture, which tend to replace organophosfate and carbamate insecticides. These pesticides have shown to exhibit cardiotoxicity. The aim of this study was to assess if cardiotoxicity is due to direct or indirect effects (metabolites) of permethrin on hearts. There were studies 8 rats; three of them were sacrificed after 24 of the end of treatment with permethrin and the other four were sacrificed after 14 days of the end of treatment. Afterwards hearts and urines were collected. The amounts of permethrin and its main metabolite (3-PBA) were evaluated on hearts and urines of female rats which were treated with permethrin and sacrificed the day after and 14 days after the treatment. Moreover has been highlighted the difference of amount of permethrin and its metabolite between rats sacrificed immediately at the end of treatment and those sacrificed after 14 days. The study of permethrin was accomplished by liquid-liquid extraction and GC-ECD. The evaluation of 3-PBA was performed by SPE procedure with 2-PBA as internal standard and gas-chromatography GC-MS. The concentration of permethrin in hearts is basically the same in 24h and 14 days. The 3-PBA concentration in urines decreased 50 times from 24h to 14 days. In hearts the 3-PBA level also decrease but only 2.24 times and a high variation of results were achieved in rats after 14 days.

Determination of permethrin and its metabolite in brains and urines of rats by GC-ECD and GC-MS

Synthetic pyrethroids are pesticides derived from naturally occurring pyrethrins, taken from pyrethrum of dried Chrysanthemum flowers. Pyrethroid insecticides are one of the most commonly used residential and agricultural insecticides. Many pyrethroids can significantly harm the nervous system. Permethrin could be one of the factors involved in the onset of neurodegenerative diseases. The present study aims to evaluate in brain, the effect that can induce the exposure to permethrin, during early life of female rats (from 6 to 21 days of life). Therefore, have been examined the concentrations of permethrin and its main metabolite (3-PBA) in the brain and urine in female rats sacrificed the day after and 14 days after treating. The different concentrations of permethrin and 3-PBA (after 24h and after 14 days in the end of treatment) were obtained using two different methods. The evaluation of permethrin by liquid-liquid extraction and GC-ECD was performed. The levels of the 3-PBA (in urine and brains) were obtained by SPE procedure and GC-MS using the 2- PBA as internal standard.

Proteomic and Transcriptomic Approaches to Abiotic Stress Tolerance in Rice (Oryza sativaL.)

Dissertação para a obtenção de grau de doutor em Biologia pelo Instituto de Tecnologia Química e Biológica da Universidade Nova de Lisboa

Integration of Membrane Filtration and Photolysis Processes for Drinking Water Treatment

Dissertation presented to obtain the Ph.D degree in Engineering and Technology Sciences, Chemical Engineering.

Valorisation of vegetable oil deodorizer distillate by enzymatic reaction and membrane processing

Dissertação para obtenção do Grau de Doutora em Engenharia Química e Bioquímica

Characterization of pesticide consumption in the county of Santarém, Pará, Brazil

Many potentially harmful pesticides for both human health and the environment are used in Brazilian Amazon. However, no scientific datum on pesticide usage is presently available for this region. Consequently, it is difficult to assess which substances arc used and in which quantities. As an important premise for future work on pesticide contamination in the county of Santarém (State of Pará, Brazil), a survey was conducted in order to qualify and quantify the use of some pesticides in this region. This investigation was made between January and March 1997 and August and October 1998 and revealed use of several organophosphates, synthetic pyrethroids and carbamates insecticides. Furthermore, many herbicides and fungicides were listed. These pesticides are used for agriculture, domestic, and sanitary programs. This paper also provides a first estimation of quantities of some insecticides commonly used in agriculture (chlorpyrifos, malathion, metamidophos and methyl-parathion). The annual consumption for these four compounds is estimated at ca. 1 910 kg. Organophosphate insecticide consumption in the county of Santarém seems to be lower than the Brazilian average in terms of «per capita» and «per agricultural area» consumptions. Nevertheless, this county uses toxic substances on sensitive environments such as floodplains (várzeas), making relevant a thorough study on the potential contamination of this environment and its biota.

Engineering of fatty acid production and secretion in Saccharomyces cerevisiae

Tese de Doutoramento em Ciências - Especialidade em Biologia

Remoção fotocatalítica de micropoluentes em meios porosos funcionalizados

Dissertação de mestrado integrado em Engenharia Civil

Aromatic amines sources, environmental impact and remediation

Aromatic amines are widely used industrial chemicals as their major sources in the environment include several chemical industry sectors such as oil refining, synthetic polymers, dyes, adhesives, rubbers, perfume, pharmaceuticals, pesticides and explosives. They result also from diesel exhaust, combustion of wood chips and rubber and tobacco smoke. Some types of aromatic amines are generated during cooking, special grilled meat and fish, as well. The intensive use and production of these compounds explains its occurrence in the environment such as in air, water and soil, thereby creating a potential for human exposure. Since aromatic amines are potential carcinogenic and toxic agents, they constitute an important class of environmental pollutants of enormous concern, which efficient removal is a crucial task for researchers, so several methods have been investigated and applied. In this chapter the types and general properties of aromatic amine compounds are reviewed. As aromatic amines are continuously entering the environment from various sources and have been designated as high priority pollutants, their presence in the environment must be monitored at concentration levels lower than 30 mg L1, compatible with the limits allowed by the regulations. Consequently, most relevant analytical methods to detect the aromatic amines composition in environmental matrices, and for monitoring their degradation, are essential and will be presented. Those include Spectroscopy, namely UV/visible and Fourier Transform Infrared Spectroscopy (FTIR); Chromatography, in particular Thin Layer (TLC), High Performance Liquid (HPLC) and Gas chromatography (GC); Capillary electrophoresis (CE); Mass spectrometry (MS) and combination of different methods including GC-MS, HPLC-MS and CE-MS. Choosing the best methods depend on their availability, costs, detection limit and sample concentration, which sometimes need to be concentrate or pretreated. However, combined methods may give more complete results based on the complementary information. The environmental impact, toxicity and carcinogenicity of many aromatic amines have been reported and are emphasized in this chapter too. Lately, the conventional aromatic amines degradation and the alternative biodegradation processes are highlighted. Parameters affecting biodegradation, role of different electron acceptors in aerobic and anaerobic biodegradation and kinetics are discussed. Conventional processes including extraction, adsorption onto activated carbon, chemical oxidation, advanced oxidation, electrochemical techniques and irradiation suffer from drawbacks including high costs, formation of hazardous by-products and low efficiency. Biological processes, taking advantage of the naturally processes occurring in environment, have been developed and tested, proved as an economic, energy efficient and environmentally feasible alternative. Aerobic biodegradation is one of the most promising techniques for aromatic amines remediation, but has the drawback of aromatic amines autooxidation once they are exposed to oxygen, instead of their degradation. Higher costs, especially due to power consumption for aeration, can also limit its application. Anaerobic degradation technology is the novel path for treatment of a wide variety of aromatic amines, including industrial wastewater, and will be discussed. However, some are difficult to degrade under anaerobic conditions and, thus, other electron acceptors such as nitrate, iron, sulphate, manganese and carbonate have, alternatively, been tested.

Persistent organic chemicals of emerging environmental concern

The use of chemicals and chemical derivatives in agriculture and industry has contributed to their accumulation and persistence in the environment. Persistent organic pollutants (POPs) are among the environmental pollutants of most concern since, when improperly handled and disposed, they can persist in the environment, bioaccumulate through the food web, and may create serious public health and environmental problems. Development of an effective degradation process has become an area of intense research. The physical/chemical methods employed, such as volatilization, evaporation, photooxidation, adsorption, or hydrolysis, are not always effective, are very expensive, and, sometimes, lead to generation/disposal of other contaminants. Biodegradation is one of the major mechanisms by which organic contaminants are transformed, immobilized, or mineralized in the environment. A clear understanding of the major processes that affect the interactions between organic contaminants, microorganisms, and environmental matrix is, thus, important for determining persistence of the compounds, for predicting in situ transformation rates, and for developing site remediation. Information on their risks and impact and occurrence in the different environmental matrices is also important, in order to attenuate their impact and apply the appropriate remediation process. This chapter provides information on the fate of pesticides and polycyclic aromatic hydrocarbons (PAHs), their impact, bioavailability, and biodegradation. © Springer Science+Business Media Dordrecht 2014.

Producción de factores de virulencia por fitopatógenos bacterianos de soja. Utilización de productos naturales como biocontrol. Production of virulence factors by soybean bacterial phytopathogens. The use of natural products as biocontrolers.

En Argentina el cultivo de soja ocupa el primer lugar en superficie sembrada. El 90% de la producción se obtiene en la zona central del pais. La siembra directa favorece la multiplicación y supervivencia de fitopatógenos causantes de tizón y pústula bacterianos. El tizón es producido por Pseudomonas syringae pv. glycinea observándose manchas marrones en las hojas. Produce gran variedad de toxinas: coronatina, faseolotoxina, siringomicina, tabtoxina, proteínas “nucleation ice”, entre otras, las cuales contribuyen a la clorosis y necrosis. En la infección, además, están involucrados exopolisacáridos (levano y alginato). La celulosa ha sido relacionada en la adhesión bacteriana y en la formación de biofilm. La pústula es causada por Xanthomonas axonopodis pv. glycines. Produce manchas pequeñas con una pequeña pústula de color claro. Libera enzimas como α-amilasa, proteasa, endo β-mannanasa, actividad peptolítica, que degradan componentes vegetales. Xantan, producido por X. axonopodis es uno de los componentes necesarios para la formación de biofilm. Este último es considerado un importante factor de virulencia porque proporciona una estrategia de colonización que otorga mayor resistencia a ambientes desfavorables, tolerancia a antimicrobianos, producción de metabolitos y exoenzimas, etc. Actualmente el control de bacterias fitopatógenas se realiza mediante pesticidas con alta toxicidad para los consumidores y el ambiente. Para evitar las bacteriosis en la práctica se sugiere la rotación de cultivos y utilizar semillas certificadas. Se están probando compuestos naturales derivados de plantas medicinales como pesticidas; estos se pueden dividir en varias categorías fitoquímicas. Varios estudios confirman la actividad antibacteriana, antifúngica y antiviral de estos productos. Extractos vegetales con alto contenido de flavonoides y aceite esenciales poseen una importante actividad antibacteriana. Además, algunos aceites esenciales podrían estar incidiendo en la liberación y/o producción de biofilm, exopolisacáridos y exoproteínas. La gran incidencia de las infecciones por fitopatógenos y las pérdidas económicas que estas acarrean hacen que su control presente grandes dificultades para la agricultura sustentable en soja de nuestro país. En este trabajo se propone estudiar los diferentes factores de virulencia de cepas bacterianas fitopatógenas y evaluar el rol que cumplen en el proceso de la enfermedad en cultivos de soja y desarrollar estrategias para el control de bacteriosis vegetales aplicando productos naturales aislados de plantas aromáticas. La correcta utilización de productos antimicrobianos de origen natural aplicados sobre el cultivo y/o sobre las semillas evitaría la dispersión de la enfermedad y la eliminación al medio ambiente de productos contaminantes no deseados. In Argentina, soybean cultivation occupies the first place; 90% of this cereal is produced in the central region of the country. Intensive tillage practices favour multiplication and survival of bacterial phytopathogens causing blight and pustule diseases. Pseudomonas syringae pv. glycinea produce several toxins like coronatine, faseolotoxine, siringomicine, tabtoxine and proteins of nucleation ice that contribute to the develop of chlorosis and necrosis, characteristic of bacterial blight. It also produces levan and alginate, cellulose and biofilm. Pustule disease is caused by Xanthomonas axonopodis pv glycines, which produce enzymes like α-amilase, protease, endo β-mannanase, peptolitic activity, xanthan and biofilm. Nowadays the control of phytopathogenic bacteria consists in the application of pesticides that are toxic for the environment and man. Natural products from medicinal plants are a new alternative for the treatment of phytopathogens. Researches made with phytochemical compounds (flavonoids, phenols, quinones, cummarines, essential oils, terpenes) support the antimicrobial activity of these natural products. What is more, these substances could suppress the biofilm, exoproteins and exopolisaccharides formation and release of them. The infections caused by phytopathogens provoke economical loses and its control presents big difficulties in our country. The proposal of this work is the characterization of phytopatoghenic strains, its virulence factors and the role they play in the disease process. The development of a new alternative for the control of vegetable bacteriosis using natural products obtained from aromatic plants and the correct application of them on sown fields or on seeds is also an objective in this work.

Percepción del riesgo de los agroquímicos en la localidad de Basavilbaso, Entre Ríos

El modelo agrario argentino actual se basa en el monocultivo de la soja para la exportación. Este cultivo aumentó de forma masiva a partir de la entrada de la soja transgénica resistente al herbicida glifosato, en los 90. Los plaguicidas han representado el gran sostén del crecimiento de la producción agropecuaria argentina. Debido al uso creciente que están teniendo y a la proximidad de los cultivos a los pueblos, los habitantes empiezan a percibir las prácticas de manejo y aplicación de plaguicidas como un riesgo para su salud y el medio ambiente de la zona. El clima de incertidumbre acerca de los impactos de los agroquímicos se percibe en las áreas productoras de soja, convirtiéndose en un conflicto entre expertos y población local. Con el estudio de este riesgo, del modo en que es percibido por la población y de los factores que causan dicha percepción, se ha observado que los problemas que generan la elevada percepción son principalmente las malas prácticas en la aplicación de los agroquímicos, la ausencia de regulación del organismo de control y la incertidumbre sobre los efectos que dichos productos pueden causar.