936 resultados para mercury preconcentration


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O Homem sempre utilizou processos produtivos com o intuito de satisfazer as suas necessidades básicas. Com o aumento da população mundial, atualmente superior a sete mil milhões de indivíduos, a quantidade de resíduos produzidos pela atividade humana, através da atividade industrial e descarga de resíduos domésticos e agrícolas, tomou dimensões desmesuradas, que são responsáveis por gerar um elevado volume de resíduos contendo diversos elementos e compostos prejudiciais ao ambiente, e, consequentemente, para a saúde humana, entre os quais se incluem alguns metais. O presente trabalho tem como principais objetivos estudar a remoção de mercúrio pela cortiça em águas sintéticas (agua MilliQ) e naturais (água de abastecimento público), na presença de outros metais (Cd, Pb e Cu) e avaliar a influência destes metais no processo de remoção. Os resultados permitiram verificar que 2,5mg/L de cortiça é uma quantidade adequada para remover mercúrio de uma solução com concentração inicial de 50μg/L de metal (percentagem de remoção de 70%), na ausência de outros contaminantes (cádmio, chumbo e cobre). Nestas condições, a quantidade máxima de mercúrio removido pela cortiça após 96 horas de contacto foi de 11,6mg de mercúrio por grama de cortiça. A presença de chumbo e cobre ou uma mistura deles reduziu a taxa de remoção de mercúrio pela cortiça e a velocidade inicial de remoção; a presença de cádmio afetou a velocidade inicial de remoção. Mesmo com a adição de outros contaminantes, como cádmio, chumbo e cobre e na presença de água de abastecimento público, observou-se que a cortiça apresenta capacidade de remoção de mercúrio. O modelo de pseudo segunda ordem foi o que apresentou um melhor ajuste aos resultados obtidos e o processo de remoção de mercúrio pela cortiça aparenta ser controlado quer pela difusão no filme quer pela difusão no poro.

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A qualidade da água degradou-se de forma relevante nas últimas décadas e os processos de sorção têm vindo a ser investigados como métodos promissores para o tratamento de águas contaminadas. Neste trabalho avaliou-se a capacidade de dois tipos de cortiça para a remoção de diversos contaminantes, em reatores de vaso fechado e de leito fixo. Os ensaios realizados em reatores de vaso fechado permitiram (i) avaliar o efeito do pH e da granulometria na eficiência dos sorventes na remoção de mercúrio e (ii) avaliar a afinidade dos sorventes para outros contaminantes, nomeadamente arsénio, cádmio, níquel e chumbo. Estruturalmente as duas cortiças estudadas aparentam ser semelhantes, com uma pequena diferença de comportamento ácido-base e não apresentam diferenças estatisticamente significativas na remoção de mercúrio. Os resultados obtidos permitiram constatar que o processo de remoção é independente do pH, tendo-se obtido percentagens de remoção da ordem dos 80% e de concentrações de mercúrio na cortiça na ordem dos 117 μg/g. As cortiças estudadas revelaram-se menos eficazes no tratamento de água com os restantes contaminantes, atingindo percentagens de remoção máximas de 0% para As, 11% para Cd, 35% para Ni e 69% para Pb. Os ensaios em leito fixo, mesmo sem terem sido otimizados, revelam que é possível obter uma eficácia de remoção de mercúrio superior a 90% nas primeiras 40 horas de trabalho, sendo a concentração de mercúrio no leito de 680 μg/g. Relativamente aos mecanismos de sorção, os resultados experimentais indicam que estes são possivelmente de natureza química e que as interações eletrostáticas têm pouca importância.

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The common cuttlefish, Sepia officinalis, is a necto-benthic cephalopod that can live in coastal ecosystems, with high influence of anthropogenic pressures and thus be vulnerable to exposure to various types of contaminants. The cuttlefish is a species of great importance to the local economy of Aveiro, considering the global data of catches of this species in the Ria de Aveiro. However, studies on this species in Ria de Aveiro are scarce, so the present study aims to fill this information gap about the cuttlefish in the Ria de Aveiro. The cuttlefish enters Ria de Aveiro in the spring and summer to reproduce, returning to deeper waters in the winter. In terms of abundance, the eastern and center regions of the lagoon, closer to the sea, showed the highest values of abundance, while the northern and southern regions of the main channel had the lowest abundance. This fact may be related to abiotic factors, as well as depth, salinity and temperature. In the most southern point of the Ria de Aveiro (Areão) no cuttlefish was caught. This site had the lowest values of salinity and depth. The cuttlefish has an allometric the females being heavier than males to mantle lengths greater than 82.4 mm. Males reach sexual maturity first than females. In Ria de Aveiro in a generation of parents was found. The cuttlefish, presents itself as opportunistic predators, consuming a wide variety of prey from different taxa. The diet was similar in different sampling locations observing significant differences for the seasons. S. officinalis was captured at 10 sites in the Ria de Aveiro with different anthropogenic sources of contamination. Thus, levels of metals analyzed were similar at all sampling sites, with the exception of a restricted area, Laranjo, which showed higher values. The cuttlefish has the ability to accumulate metals in your body. The levels of Fe, Zn, Cu, Cd, Pb and Hg found in the digestive gland and mantle reflect a differential accumulation of metals in the tissues. This accumulation is related to the type and function of tissue analyzed and the type of metal analysis (essential and non-essential). The metal concentrations in the digestive gland are higher than in the mantle, with the exception of mercury. This may be due to the high affinity of the mantle for the incorporation of methylmercury (MeHg), the most abundant form of mercury. The accumulation of metals can vary over a lifetime, depending on the metal. The concentrations of Zn, Cd and Hg increases throughout life, while Pb decreases and essential metals such as Fe and Cu remain constant. The data collected suggest that the cuttlefish (Sepia officinalis) can be used as a bioindicator of environmental contamination for some metals.

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Para o ser humano, a água sempre foi um recurso essencial ao longo da sua evolução. Hoje em dia, com todo o avanço tecnológico, a água é um bem muito vulnerável às diversas atividades antropogénicas. Entre os muitos contaminantes que podem afetar a qualidade da água para consumo humano, os metais causam grande preocupação devido à sua elevada toxicidade. O mercúrio é um dos contaminantes que deve ser devidamente controlado devido ao seu elevado grau de toxicidade. Este Estágio foi realizado no Laboratório Luságua e o seu principal objetivo foi avaliar se era possível baixar o limite de quantificação da técnica existente na empresa para quantificar o mercúrio em águas de consumo e validar o método através do cálculo de vários parâmetros de controlo de qualidade. Foi ainda feita a comparação entre a técnica de quantificação de mercúrio existente na Luságua (CV-AAS) e a existente na Universidade de Aveiro (CVAFS) para avaliar se havia uma mais-valia para a Luságua se adquirisse um novo equipamento para analisar o mercúrio em águas. Os parâmetros de validação avaliados nos dois métodos derem resultados semelhantes, não identificando a necessidade atual de substituir o equipamento existente na Luságua, até porque se conseguiu baixar o limite de quantificação, atingindo assim o objetivo estabelecido no início para este Estágio.

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The present work reports the study of the bioaccumulation of potentially toxic elements (cadmium, lead and mercury) by marine macroalgae (Ulva lactuca, Fucus vesiculosus and Gracilaria gracilis), abundant in the coast and estuarine systems worldwide. These organisms proved to be capable of withstanding moderate multi-metallic contamination (environmentally relevant concentrations), incorporating high amounts of metal in their tissues. The high removal percentages achieved, in particular for mercury (99%), demonstrate the potential of these algae as a basis for a new biotechnological treatment of saline waters contaminated with metals (more efficient, cost-effective and environmentally friendly than conventional methods). U. lactuca was considered the most promising due to the better performance presented. The comparison between the bioaccumulation and biosorption processes suggested that in some cases the use of the living organism will have advantages over the application of biomass, due to the simplicity of the overall process, and the lower residual concentration of metal achieved in the solution (especially for Cd). The transfer and accumulation of Hg by terrestrial plants (Brassica juncea and Lolium perenne) in agricultural fields near a contaminated industrial area was also studied. Despite the low bioaccumulation factors found (<1), there were high Hg content in plants (up to 84 mg kg-1 in roots and up 6.9 mg kg-1 in shoots, dry weight). Daily intake estimates for grazing animals (cows and sheep) pointed to the potential risk to human health derived from consumption of their meat. The results highlighted the important role that plants and algae may have in protection, risk assessment and remediation of environmental systems contaminated with metals.

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Endocrine disruptors and pharmaceuticals are considered to be concerning environmental contaminants. During the last two decades, studies dealing with the occurrence and fate of these emerging contaminants in the aquatic environment have raised attention and its number is constantly increasing. The presence of these contaminants in the environment is particularly important since they are known to induce adverse effects in the ecosystems even at extremely low concentrations. Estrogens and antibiotics, in particular, are identified as capable of induce endocrine disruption and contribute for the appearance of multi-resistant bacteria, respectively. A better assessment and understanding of the real impact of these contaminants in the aquatic environment implies the evaluation of their occurrence and fate, which is the main aim of this Thesis. Two estrogens (17-estradiol and 17-ethinylestradiol) and an antibiotic (sulfamethoxazole) were the contaminants under study and their occurrence in surface and waste waters was assessed by the implementation of enzyme linked immunosorbent assays (ELISAs). The assays were optimized in order to accomplish two important aspects: to analyze complex water samples, giving special attention to matrix effects, and to increase the sensitivity. Since the levels of these contaminants in the environment are extremely low, a pre-concentration methodology was also object of study in this Thesis. Dispersive liquid-liquid microextraction (DLLME) was developed for the preconcentration of E2 and EE2, subsequently quantified by either highperformance liquid chromatography (HPLC) and the previously optimized ELISAs. Moreover, the use of anthropogenic markers, i.e. indicators of human presence or activity, has been discussed as a tool to track the origin and type of contamination. An ELISA for the quantification of caffeine, as an anthropogenic marker, was also developed in order to assess the occurrence of human domestic pollution in Portuguese surface waters. Finally, photodegradation is considered to be one of the most important pathways contributing for the mitigation of pollutants’ presence in the aquatic environment. Both direct and indirect photodegradation of E2 and EE2 were evaluated. Since the presence of humic substances (HS) is known to have a noticeable influence on the photodegradation of pollutants and in order to mimic the real aquatic environment, special attention was given to the influence of the presence and concentration of different fractions of HS on the photodegradation of both hormones.

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Esta dissertação está dividida em duas partes. Na primeira parte reportam-se métodos de síntese de (E)-3-estirilflavonas e (E)/(Z)-2-aril- 4-cloro-3-estiril-2H-cromenos e estudos de ciclização das (E)-3- estirilflavonas em 5-arilbenzo[c]xantonas. Na segunda parte desenvolveram-se novas rotas de síntese de (E)-2-aril-3-estiril-4- quinolonas e posterior transformação em 5-fenil-12- metilbenzo[c]acridonas e 2,4-diarilfuro[3,2-c]quinolinas. Nesta parte estudou-se também a transformação de 2-aril-4-cloro-1,2-dihidroquinolina- 1,3-dicarbaldeídos em (E)/(Z)-2-aril-4-cloro-3-estiril-1,2- di-hidroquinolina-1-carbaldeídos. A síntese de novos derivados de (E)-3-estirilflavonas, abordada na primeira parte desta dissertação, envolveu estudos de otimização da reação de bromação seguida de ciclização de 3-aril-1-(2- hidroxiaril)propano-1,3-dionas/3-aril-3-hidroxi-1-(2-hidroxiaril)prop-2- en-1-onas em 3-bromoflavonas e o desenvolvimento de uma nova rota de síntese de 3-metilflavonas. As 3-metilflavonas foram sujeitas a bromação e seguidamente transformadas em sais de fosfónio antes de serem utilizadas na síntese de (E)-3-estirilflavonas via reação de Wittig. As 3-bromoflavonas foram também usadas na síntese de (E)-3- estirilflavonas via reação de Heck. A síntese de novos derivados de (E)/(Z)-2-aril-4-cloro-3-estiril-2H-cromenos, via reação de Wittig, envolveu a síntese e formilação de flavanonas. A última transformação reportada na primeira parte desta dissertação é a síntese de 5-arilbenzo[c]xantonas por reação de eletrociclização seguida de oxidação de (E)-3-estirilflavonas. Na segunda parte desta dissertação são estudadas duas vias de síntese de 2-aril-1-metil-4-quinolonas. A primeira via de síntese envolve a síntese de N-(2-acetilfenil)benzamidas, sua ciclização em 4-quinolonas seguida de metilação destas. A segunda via envolve a metilação e ciclização de N-(2-acetilfenil)benzamidas obtendo-se, num só passo, as 2-aril-1-metil-4-quinolonas. Posterior iodação das 2-aril-1-metil-4- quinolonas e subsequente reação de Heck das 2-aril-3-iodo-1-metil-4- quinolonas com estirenos comerciais possibilitaram a síntese de (E)-2- aril-3-estiril-1-metil-4-quinolonas. Estudos de eletrociclização seguidos de oxidação das (E)-2-aril-3-estiril-1-metil-4-quinolonas utilizando uma lâmpada de UV de mercúrio de alta pressão possibilitou a síntese de 5- fenil-12-metilbenzo[c]acridonas, enquanto que o aquecimento em refluxo de 1,2,4-triclorobenzeno deu origem a 2,4-diarilfuro[3,2- c]quinolinas. Nesta segunda parte aborda-se também a síntese de 2-aril-4-cloro-1,2- di-hidroquinolina-1,3-dicarbaldeídos, a partir da formilação de 2-aril- 2,3-di-hidro-4-quinolonas e a sua transformação em (E)/(Z)-2-aril-4- cloro-3-estiril-1,2-di-hidroquinolina-1-carbaldeídos por reação de Wittig. Todos os compostos sintetizados foram caracterizados por espectroscopia de ressonância magnética nuclear de protão e carbono 13C, espectros bidimensionais de correlação heteronuclear (HMBC e HSQC) e, nalguns casos espectros de efeito nuclear Overhauser (NOESY). Os novos produtos foram igualmente caracterizados por espectrometria de massa e sempre que possível análise elementar ou espectrometria de massa de alta resolução.

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We have developed a new method for single-drop microextraction (SDME) for the preconcentration of organochlorine pesticides (OCP) from complex matrices. It is based on the use of a silicone ring at the tip of the syringe. A 5 μL drop of n-hexane is applied to an aqueous extract containing the OCP and found to be adequate to preconcentrate the OCPs prior to analysis by GC in combination with tandem mass spectrometry. Fourteen OCP were determined using this technique in combination with programmable temperature vaporization. It is shown to have many advantages over traditional split/splitless injection. The effects of kind of organic solvent, exposure time, agitation and organic drop volume were optimized. Relative recoveries range from 59 to 117 %, with repeatabilities of <15 % (coefficient of variation) were achieved. The limits of detection range from 0.002 to 0.150 μg kg−1. The method was applied to the preconcentration of OCPs in fresh strawberry, strawberry jam, and soil.

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Disposable screen-printed electrodes (SPCE) were modified using a cosmetic product to partially block the electrode surface in order to obtain a microelectrode array. The microarrays formed were electropolymerized with aniline. Scanning electron microscopy was used to evaluate the modified and polymerized electrode surface. Electrochemical characteristics of the constructed sensor for cadmium analysis were evaluated by cyclic and square-wave voltammetry. Optimized stripping procedure in which the preconcentration of cadmium was achieved by depositing at –1.20 V (vs. Ag/AgCl) resulted in a well defined anodic peak at approximately –0.7 V at pH 4.6. The achieved limit of detection was 4 × 10−9 mol dm−3. Spray modified and polymerized microarray electrodes were successfully applied to quantify cadmium in fish sample digests.

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The electroactivity of butylate (BTL) is studied by cyclic voltammetry (CV) and square wave voltammetry (SWV) at a glassy carbon electrode (GCE) and a hanging mercury drop electrode (HMDE). Britton–Robinson buffer solutions of pH 1.9–11.5 are used as supporting electrolyte. CV voltammograms using GCE show a single anodic peak regarding the oxidation of BTL at +1.7V versus AgCl/ Ag, an irreversible process controlled by diffusion. Using a HMDE, a single cathodic peak is observed, at 1.0V versus AgCl/Ag. The reduction of BTL is irreversible and controlled by adsorption. Mechanism proposals are presented for these redox transformations. Optimisation is carried out univaryingly. Linearity ranges were 0.10–0.50 mmol L-1 and 2.0–9.0 µmolL-1 for anodic and cathodic peaks, respectively. The proposed method is applied to the determination of BTL in waters. Analytical results compare well with those obtained by an HPLC method.

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The reduction of luvastatin (FLV) at a hanging mercury-drop electrode (HMDE) was studied by square-wave adsorptive-stripping voltammetry (SWAdSV). FLV can be accumulated and reduced at the electrode, with a maximum peak current intensity at a potential of approximately 1.26V vs. AgCl=Ag, in an aqueous electrolyte solution of pH 5.25. The method shows linearity between peak current intensity and FLV concentration between 1.0 10 8 and 2.7 10 6 mol L 1. Limits of detection (LOD) and quantification (LOQ) were found to be 9.9 10 9 mol L 1 and 3.3 10 8 mol L 1, respectively. Furthermore, FLV oxidation at a glassy carbon electrode surface was used for its hydrodynamic monitoring by amperometric detection in a flow-injection system. The amperometric signal was linear with FLV concentration over the range 1.0 10 6 to 1.0 10 5 mol L 1, with an LOD of 2.4 10 7 mol L 1 and an LOQ of 8.0 10 7 mol L 1. A sample rate of 50 injections per hour was achieved. Both methods were validated and showed to be precise and accurate, being satisfactorily applied to the determination of FLV in a commercial pharmaceutical.

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A methodology for the determination of the pesticide chlorfenvinphos by microwave-assisted solvent extraction and square-wave cathodic stripping voltammetry at a mercury film ultramicroelectrode in soil samples is proposed. Optimization of microwave solvent extraction performed with two soils, selected for having significantly different properties, indicated that the optimum solvent for extracting chlorfenvinphos is hexane-acetone (1:1, v/v). The voltammetric procedure is based on controlled adsorptive accumulation of the insecticide at the potential of -0.60 V (vs. Ag/AgCl) in the presence of Britton-Robinson buffer (pH 6.2). The detection limit obtained for a 10 s collection time was 3.0 x 10-8 mol l-1. The validity of the developed methodology was assessed by recovery experiments at the 0.100 µg g-1 level. The average recoveries and standard deviations for the global procedure reached byMASE-square-wave voltammetry were 90.2±2.8% and 92.1±3.4% for type I (soil rich in organic matter) and type II (sandy soil) samples, respectively. These results are in accordance to the expected values which show that the method has a good accuracy.

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In this work we isolated from soil and characterized several bacterial strains capable of either resisting high concentrations of heavy metals (Cd2+ or Hg2+ or Pb2+) or degrading the common soil and groundwater pollutants MTBE (methyl-tertbutyl ether) or TCE (trichloroethylene). We then used soil microcosms exposed to MTBE (50 mg/l) or TCE (50 mg/l) in the presence of one heavy metal (Cd 10 ppm or Hg 5 ppm or Pb 50 or 100 ppm) and two bacterial isolates at a time, a degrader plus a metalresistant strain. Some of these two-membered consortia showed degradation efficiencies well higher (49–182% higher) than those expected under the conditions employed, demonstrating the occurrence of a synergetic relationship between the strains used. Our results show the efficacy of the dual augmentation strategy for MTBE and TCE bioremediation in the presence of heavy metals.

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The treatment efficiency of laboratory wastewaters was evaluated and ecotoxicity tests with Chlorella vulgaris were performed on them to assess the safety of their environmental discharge. For chemical oxygen demand wastewaters, chromium (VI), mercury (II) and silver were efficiently removedby chemical treatments.Areduction of ecotoxicitywas achieved; nevertheless, an EC50 (effective concentration that causes a 50% inhibition in the algae growth) of 1.5% (v/v) indicated still high level of ecotoxicity. For chloride determination wastewaters, an efficient reduction of chromium and silver was achieved after treatment. Regarding the reduction of ecotoxicity observed, EC50 increased from 0.059% to 0.5%, only a 0.02% concentration in the aquatic environment would guarantee no effects. Wastewaters containing phenanthroline/iron (II) complex were treated by chemical oxidation. Treatmentwas satisfactory concerning chemical parameters, although an increase in ecotoxicitywas observed (EC50 reduced from 0.31% to 0.21%). The wastes from the kinetic study of persulphate and iodide reaction were treated with sodium bisulphite until colour was removed. Although they did not reveal significant ecotoxicity, only over 1% of the untreated waste produced observable effects over algae. Therefore, ecotoxicity tests could be considered a useful tool not only in laboratory effluents treatment, as shown, but also in hazardous wastewaters management.

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The electrochemical behavior of citalopram was studied by square-wave and square-wave adsorptive-stripping voltammetry (SWAdSV). Citalopram can be reduced and accumulated at a mercury drop electrode, with a maximum peak current intensity being obtained at a potential of approximately -1.25V vs. AgCl/Ag, in an aqueous electrolyte solution of pH 12. A SWAdSV method has been developed for the determination of citalopram in pharmaceutical preparations. The method shows a linear range between 1.0x10-7 and 2.0x10-6 mol L-1 with a limit of detection of 5x10-8 mol L-1 for an accumulation time of 30 s. The precision of the method was evaluated by assessing the repeatability and intermediate precision, achieving good relative standard deviations in all cases (≤2.3%). The proposed method was applied to the determination of citalopram in five pharmaceutical products and the results obtained are in good agreement with the labeled values.