Distribuição dos metais nas poeiras colhidas em Estarreja: estudo da mobilidade e impacto potencial dos metais no ambiente

As poeiras urbanas, vulgarmente designadas na literatura por street dusts ou road dusts, são misturas heterogêneas de partículas minerais do solo e partículas resultantes do tráfego, formando um material com características únicas e específicas de cada local. Estas partículas, geralmente enriquecidas com elementos potencialmente tóxicos, quando inaladas ou ingeridas poderão ser um risco para a saúde das populações. Neste trabalho foram recolhidas 21 amostras de poeiras urbanas na cidade de Estarreja assim como amostras representativas de partículas relacionados com o tráfego (poeiras resultante do desgaste dos travões e das marcações dos pavimentos e estradas) com o objetivo de investigar a contribuição relativa destas partículas no comportamento geoquímico dessas amostras e o risco associado para as populações locais. Para a concretização do objetivo proposto caracterizou-se química e mineralogicamente as amostras de poeiras urbanas e as partículas relacionadas com o tráfego e avaliou-se a disponibilidade e bioacessibilidade para três elementos considerados potencialmente tóxicos (Cu, Pb e Zn) usando uma combinação de ensaios: (a) digestão ácida; (b) extração sequencial para identificar o fracionamento do Cu, Pb e Zn nas diferentes fases-suporte dos metais, e (c) bioaccessibilidade oral in vitro. Os resultados da análise química mostram que as poeiras dos travões apresentam concentrações elevadas em Fe, Cu, Zn, Mn, Ba, Sb, Cr e Ni sendo de referir diferenças composicionais significativas entre as amostras estudadas. A amostra de tinta contém teores elevados de Ba, Ca, Ti e Pb e também pode conter outros elementos tais como Co, Cr, Cu, Mn. Mineralogicamente constata-se que as amostras de poeiras dos travões tem uma composição mineralógica semelhante mostrando que são constituídas por uma elevada percentagem de material de baixa cristalinidade, grafite e óxidos/hidróxidos de Fe amorfos. A amostra de tinta de marcação dos pavimentos das estradas é composta por material mais cristalino do que a poeira dos travões e é essencialmente constituída por carbonatos (maioritariamente dolomite) e também por barite (em menor quantidade). Os resultados obtidos nas amostras de poeiras urbanas indicam a existência de associações de elementos que definem claramente a componente geogénica e/ou antropogénica e apontam para diferenças entre essas associações nas duas frações estudadas (250 m e 63 m). A heterogeneidade das poeiras é revelada pela existência de partículas com origem geogénica (por exemplo quartzo e aluminossilicatos), de partículas com características marcadamente antropogénicas (partículas enriquecidas em Fe, Pb, Zn e Cu) ou ainda de partículas com origem mista (óxidos de Fe e Ti). Os resultados da extração química seletiva sequencial permitiu concluir que, nas amostras em estudo, as fases de troca e ácido-solúveis são as fases suporte mais importantes para o Cu, Pb e Zn Os resultados dos ensaios de bioacessibilidade mostraram também que uma percentagem significativa de Cu, Pb e Zn total está disponível para absorção gástrica. Este estudo destaca também a necessidade de se caracterizar em detalhe as propriedades intrínsecas das partículas antrópicas presentes nas poeiras urbanas, de forma a compreender as variações da fração bioacessível nos diferentes elementos estudados assim como nas diferentes frações.

Catalytic routes to convert saccharides to furanic aldehydes

The conversion of plant biomass-derived carbohydrates (preferably non-edible) into added-value products is envisaged to be at the core of the future biorefineries. Carbohydrates are the most abundant natural organic polymers on Earth. This work deals with the chemical valorisation of plant biomass, focusing on the acid-catalysed conversion of carbohydrates (mono and polysaccharides) to furanic aldehydes, namely 2-furaldehyde (Fur) and 5-hydroxymethyl-2-furaldehyde (Hmf), which are valuable platform chemicals that have the potential to replace a variety of oil derived chemicals and materials. The investigated reaction systems can be divided into two types depending on the solvent used to dissolve the carbohydrates in the reaction medium: water or ionic liquid-based systems. The reaction temperatures were greater than 150 ºC when the solvent was water, and lower than 150 º C in the cases of the ionic liquid-based catalytic systems. As alternatives to liquid acids (typically used in the industrial production of Fur), solid acid catalysts were investigated in these reaction systems. Aiming at the identification of (soluble and insoluble) reaction products, complementary characterisation techniques were used namely, FT-IR spectroscopy, liquid and solid state NMR spectroscopy, TGA, DSC and GC´GC-ToFMS analyses. Complex mixtures of soluble reaction products were obtained and different types of side reactions may occur. The requirements to be put on the catalysts for these reaction systems partly depend on the type of carbohydrates to be converted and the reaction conditions used. The thermal stability is important due to the fact that formation of humins and catalyst coking phenomena are characteristically inherent to these types of reactions systems leading to the need to regenerate the catalyst which can be effectively accomplished by calcination. Special attention was given to fully inorganic nanoporous solid acids, amorphous or crystalline, and consisting of nano to micro-size particles. The investigated catalysts were silicoaluminophosphates, aluminosilicates and zirconium-tungsten mixed oxides which are versatile catalysts in that their physicochemical properties can be fine-tuned to improve the catalytic performances in the conversion of different substrates (e.g. introduction of mesoporosity and modification of the acid properties). The catalytic systems consisting of aluminosilicates as solid acids and water as solvent seem to be more effective in converting pentoses and related polysaccharides into Fur, than hexoses and related polysaccharides into Hmf. The investigated solid acids exhibited fairly good hydrothermal stabilities. On the other hand, ionic liquid-based catalytic systems can allow reaching simultaneously high Fur and Hmf yields, particularly when Hmf is obtained from D-fructose and related polysaccharides; however, catalyst deactivation occurs and the catalytic reactions take place in homogeneous phase. As pointed out in a review of the state of the art on this topic, the development of truly heterogeneous ionic liquid-based catalytic systems for producing Fur and Hmf in high yields remains a challenge.

Characterization of water-soluble organic compounds in bioaerosols by liquid chromatography and fluorescence spectroscopy

In the last decades, the effects of the air pollution have been increasing, especially in the case of the human health diseases. In order to overcome this problem, scientists have been studying the components of the air. As a part of water-soluble organic compounds, amino acids are present in the atmospheric environment as components of diverse living organisms which can be responsible for spreading diseases through the air. Liquid chromatography is one technique capable of distinguish the different amino acids from each other. In this work, aiming at separating the amino acids found in the aerosols samples collected in Aveiro, the ability of four columns (Mixed-Mode WAX-1, Mixed-Mode HILIC-1, Luna HILIC and Luna C18) to separate four amino acids (aspartic acid, lysine, glycine and tryptophan) and the way the interaction of the stationary phases of the columns with the analytes is influenced by organic solvent concentration and presence/concentration of the buffer, are being assessed. In the Mixed-Mode WAX-1 column, the chromatograms of the distinct amino acids revealed the separation was not efficient, since the retention times were very similar. In the case of lysine, in the elution with 80% (V/V) MeOH, the peaks appeared during the volume void. In the Mixed-Mode HILIC-1 column, the variation of the organic solvent concentration did not affect the elution of the four studied amino acids. Considering the Luna HILIC column, the retention times of the amino acids were too close to each other to ensure a separation among each other. Lastly, the Luna C18 column revealed to be useful to separate amino acids in a gradient mode, being the variation of the mobile phase composition in the organic solvent concentration (ACN). Luna C18 was the column used to separate the amino acids in the real samples and the mobile phase had acidified water and ACN. The gradient consisted in the following program: 0 – 2 min: 5% (V/V) ACN, 2 – 8 min: 5 – 2 % (V/V) ACN, 8 – 16 min: 2% (V/V) ACN, 16 – 20 min: 2 – 20 % (V/V) ACN, 20 – 35 min: 20 – 35 % (V/V) ACN. The aerosols samples were collected by using three passive samplers placed in two different locations in Aveiro and each sampler had two filters - one faced up and the other faced down. After the sampling, the water-soluble organic compounds was extracted by dissolution in ultra-pure water, sonication bath and filtration. The resulting filtered solutions were diluted in acidified water for the chromatographic separation. The results from liquid chromatography revealed the presence of the amino acids, although it was not possible to identify each one of them individually. The chromatograms and the fluorescence spectra showed the existence of some patterns: the samples that correspond to the up filters had more intense peaks and signals, revealing that the up filters collected more organic matter.