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Solid phase extraction is one of the most widely used methods to concentrate diluted compounds in a solution. Substances can be extracted into admicelles and hemimicelles, which are surface adsorbed micelles and surfactant monolayers, respectively. Investigations of the electrical control of surfactants on surfaces for the purpose of analyte preconcentration prior to chromatographic analysis are presented. The surfactant layer serves as the “stationary phase” in a solid phase extraction sorbent scenario. Analytes are adsorbed on this layer, and then released from the solid phase via surfactant removal. The attachment and removal of the surfactant are controlled by means of an electric field. Because the surfactant-analyte association is released by electrical control, organic solvents, which are used in conventional solid phase extraction, are not required. Therefore, this procedure is advantageous for method development and environmental concerns. Presented is the preconcentration of a test probe, 2-naphthol, using electrical control of the formation and release of dodecyl sulfate on planar gold, gold coated stainless steel, and a porous stainless steel frit, using impedance spectroscopy to observe the layer formation with various surfactant concentrations and applied potentials.

Η απορρύπανση των υδάτων αποτελεί αναγκαία και καθιερωμένη από δεκαετίες πρακτική. Η απορρύπανση με τη μέθοδο της ρόφησης είναι μία από την πληθώρα των τεχνικών που εφαρμόζονται. Το περισσότερο διαδεδομένο ροφητικό υλικό είναι ο ενεργός άνθρακας, του οποίου όμως το υψηλό κόστος παραγωγής, οδήγησε την επιστημονική έρευνα στην αναζήτηση εναλλακτικών, υλικών χαμηλότερου κόστους. Για το σκοπό αυτό, το επιστημονικό ενδιαφέρον έχει στραφεί σε πολλά υλικά κυρίως οργανικής προέλευσης, αλλά και σε ανόργανα υλικά, όπως τα οξείδια των μετάλλων, τα οποία αφθονούν στη φύση. Στην παρουσα εργασία έγινε μελέτη της ροφητικής ικανότητας φυσικών οξειδίων, για τη ρόφηση αρωματικών οργανικών ενώσεων και βαρέων μετάλλων. Πιο συγκεκριμένα, μελετήθηκε ο μηχανισμός της ρόφησης του φαινανθρενίου, της 2-ναφθόλης και του υδραργύρου από οξείδια αργιλίου, τιτανίου, αργιλίου/πυριτίου και σιδήρου, με σκοπό την αξιολόγηση των υλικών αυτών ως ροφητικών υλικών και τη σύγκριση των αποτελεσμάτων με αυτά της ρόφησης των αντίστοιχων ρύπων από υλικά που παρασκευάζονται από την πυρόλυση πρώτης ύλης βιολογικής προέλευσης. Για τη μελέτη της κινητικής της ρόφησης του φαινανθρενίου και της 2-ναφθόλης πραγματοποιήθηκαν πειράματα σε θερμοκρασία περιβάλλοντος, σε θαλασσινό και γλυκό συνθετικό νερό, με διαφορετικές ποσότητες ροφητικού υλικού (χωρίς χημική επεξεργασία) και για διαφορετικό χρόνο επαφής. Από τα πειράματα αυτά μετρήθηκε η κινητική της ρόφησης καθώς και το ποσοστό απομάκρυνσης των ρύπων από το διάλυμα. Από τις μετρήσεις που έγιναν, προέκυψε ότι το ποσοστό απομάκρυνσης του φαινανθρενίου από το διάλυμα αυξάνεται αυξανομένης της ποσότητας του ροφητικού υλικού. Η σταθερά της ρόφησης Kd, κυμάνθηκε σε ένα εύρος τιμών από 1 έως 10 L/Kg, τιμές 2 έως 4 τάξεις μεγέθους μικρότερες από αυτές άλλων ροφητικών υλικών βιολογικής προέλευσης, ή προϊόντων πυρόλυσης. Τη μεγαλύτερη ικανότητα ρόφησης φαινανθρενίου επέδειξε η γ-αλούμινα με ειδική επιφάνεια 270 m2/g, με μέγιστη απομάκρυνση φαινανθρενίου το 55 % της αρχικής συγκέντρωσης έπειτα από 8 ημέρες, ενώ τη μικρότερη ικανότητα ρόφησης η γ-αλούμινα με ειδική επιφάνεια 120 m2/g, με μέγιστη απομάκρυνση το 14 % της αρχικής συγκέντρωσης, έπειτα από 10 ημέρες. Η τιτάνια, με ειδική επιφάνεια 120 m2/g, είχε ως αποτέλεσμα την απομάκρυνση του 52 % της αρχικής συγκέντρωσης φαινανθρενίου, σε 8 ημέρες. Από τα πειράματα ρόφησης της 2-ναφθόλης από την γ-αλούμινα, δεν προέκυψε μετρήσιμη ρόφηση. Η ρόφηση του υδραργύρου από την γ-αλούμινα (ειδική επιφάνεια 131 m2/g), και τα οξείδια σιδήρου μελετήθηκε με πειράματα στους 25 °C, σε pH 5 και με χρόνο εξισορρόπησης τις 24 h. Από τα πειράματα προέκυψε ισόθερμη καμπύλη και έγινε προσπάθεια προσαρμογής της σε μοντέλα ρόφησης. Παρατηρήθηκε αύξηση του ποσοστού απομάκρυνσης του υδραργύρου, με αύξηση της μάζας της γ-αλούμινας. Το μέγιστο ποσοστό απομάκρυνσης, ήταν το 93 % της αρχικής συγκέντρωσης και επιτεύχθηκε με μάζα γ-αλούμινας ίση και μεγαλύτερη από 1 g. Για τιμή Ce=15 mg/L, μετρήθηκε qe=0,91 mg/g, τιμή 1 έως 2 τάξεις μεγέθους μικρότερη από αυτές άλλων ροφητικών υλικών βιολογικής προέλευσης ή προϊόντων πυρόλυσης. Τα οξείδια σιδήρου, παρότι είχαν ειδική επιφάνεια 55 m²/g, δεν παρουσίασαν μετρήσιμη ροφητική ικανότητα για κανέναν από τους ρύπους, που μελετήθηκαν στην παρούσα εργασία. Συνοψίζοντας μπορούμε να πούμε ότι τα ανόργανα υλικά που μελετήθηκαν στην παρούσα εργασία, παρόλο που παρουσιάζουν μεγάλες τιμές ειδικής επιφάνειας, δεν μπορούν να χαρακτηρισθούν ως αξιόλογα ροφητικά υλικά, τόσο για τη ρόφηση των οργανικών ρύπων φαινανθρένιο και 2-ναφθόλη, όσο και για τη ρόφηση του υδραργύρου. / Water treatment is a necessary and standard practice since decades. Adsorption technology in water treatment is one of many techniques being used. Activated carbon is the most widely applied adsorbent in water treatment, however its high production cost has led scientific research to investigate alternative low cost sorbent materials. This need has developed scientific interest towards novel materials most of them derived from biomass, but also inorganic oxides that are abundant in nature. The present study focuses on the investigation of the capacity of natural oxides to adsorb aromatic organic compounds and heavy metals. Specifically, sorption of phenanthrene, 2-naphthol and mercury onto aluminum, titanium, silicon and ferric oxides was examined, for the evaluation of these materials as sorbents, compared to pyrolized biomaterials. For the study of sorption of phenanthrene and 2-naphthol, batch experiments were conducted at room temperature, using artificial seawater and fresh water, different mass of sorbent material at different contact time. Sorption kinetics and the pollutant removal percentages were determined. The proportion of phenanthrene removal increased with the increase of the mass of the sorbent material. Sorption distribution coefficient Kd ranged between 1 and 10 L/Kg. These values are 2 to 4 orders of magnitude lower than the respective values shown for biomaterials and for pyrolysis products, respectively. Maximum sorption capacity of phenanthrene (55 % proportion removal) was shown by γ-alumina, with a specific surface area equal to 270 m2/g, after 8 days. Minimum sorption capacity (14 % proportion removal) was shown by γ-alumina, with a specific surface area equal to 120 m2/g, after 10 days. Titania, with a specific surface area equal to 120 m2/g, adsorbed a proportion of 52 % of the initial concentration of phenanthrene, after 8 days. Sorption experiments of 2-naphthol from γ-alumina, did not show a measurable sorption. Sorption of mercury from γ-alumina and ferric oxides was studied, conducting batch experiments at 25 °C, pH 5, 24 h contact time. The experiments resulted to an isotherm curve that was evaluated using different sorption isotherm models. An increase of the proportion of mercury removal, with the increase of the mass of γ-alumina was observed. Maximum proportion of mercury removal (93% of the initial concentration) was observed with the addition of γ-alumina of 1 g or more. At Ce=15 mg/L, qe=0,91 mg/g was measured. This value is 1 to 2 orders of magnitude lower, than the respective values shown for biomaterials and for pyrolysis products, respectively. Even though ferric oxides’ specific surface area was estimated at 55 m²/g, they did not show a measurable sorption capacity for any of the pollutants tested in the present study. Even though the materials examined in the present study, were of large specific surface area, their sorptive properties shown, are not competitive with the respective properties of biomaterials. Thus, they cannot be considered as promising sorbents for the removal of phenanthrene, 2-naphthol, or mercury from water.

Submitted by Ana Hilda Fonseca (anahilda@ufba.br) on 2014-09-17T17:51:04Z No. of bitstreams: 1 (Dissertação_mestrado__(03.11_)).pdf: 1756144 bytes, checksum: 6a5c8a2f486f154eba91b5aa9780dde0 (MD5) / Approved for entry into archive by Fatima Cleômenis Botelho Maria (botelho@ufba.br) on 2014-09-19T12:24:04Z (GMT) No. of bitstreams: 1 (Dissertação_mestrado__(03.11_)).pdf: 1756144 bytes, checksum: 6a5c8a2f486f154eba91b5aa9780dde0 (MD5) / Made available in DSpace on 2014-09-19T12:24:04Z (GMT). No. of bitstreams: 1 (Dissertação_mestrado__(03.11_)).pdf: 1756144 bytes, checksum: 6a5c8a2f486f154eba91b5aa9780dde0 (MD5) / CNPQ / A determinação de metais em águas naturais por Espectrometria de Emissão Óptica com Plasma Indutivamente Acoplado (ICP OES), em geral, deve envolver etapas de pré- concentração, devido os níveis de concentração dos metais em água serem muitas vezes abaixo dos limites de detecção da técnica. Dessa forma, o objetivo desse trabalho foi desenvolver um método de pré-concentração em fase sólida sensível e simples para a determinação de cobre, ferro, níquel, manganês, chumbo e zinco em amostras de água por ICP OES. As condições experimentais para pré-concentração foram otimizadas considerando os fatores: concentração do eluente, volume de eluente, volume da amostra, vazão e pH. As condições otimizadas corresponderam ao uso de 5 mL de solução de HCl 0,8 mol L-1 como eluente, volume da amostra de 50 mL, vazão de 1,9 mL min-1 e pH 9,0. Para a determinação dos metais, as amostras, após ajuste do pH, foram percoladas com o auxílio de uma bomba peristáltica em cartucho Sep-pak C18 com 1-(2-piridilazo)-2-naftol (PAN) imobilizado na sílica funcionalizada C18. A eluição dos analitos foi realizada com a passagem da solução de HCl pelo cartucho para posterior determinação por ICP OES. Nestas condições, os limites de detecção para Cu, Fe, Mn, Ni, Pb e Zn obtidos variaram entre 0,11 e 21 µg L-1 e os limites de quantificação entre 0,36-69 µg L-1, respectivamente. Os desvios padrão relativos (R.S.D.) para a determinação dos analitos não ultrapassaram 9 %. O efeito de possíveis espécies interferentes sobre a recuperação dos analitos também foram investigados. A exatidão do método foi avaliada mediante análise de material de referência certificado (SLEW-3 Estuariene Water Reference Material for Trace Metals) e o método proposto foi aplicado para análise de amostras de água subterrânea, água potável e água de rio coletadas nos municípios de Cachoeira e São Félix, Bahia, Brasil. As amostras foram analisadas por Espectrometria de Massas com Plasma Indutivamente Acoplado (ICP-MS) como método comparativo, não sendo observadas diferenças significativas entre estes resultados e os resultados obtidos pelo método proposto. / The determination of metals in natural waters by Inductively Coupled Plasma Optical Emission Spectrometry (ICP OES), in general, involves pre-concentration steps, due the concentration levels of metals in water are often below the limits of detection of this technique. In this way, the objective of this work was to develop a pre-concentration solid phase method for sensitive and simple determination of copper, iron, nickel, manganese, lead and zinc in water samples by ICP OES. The experimental conditions for pre- concentration were optimized considering the following factors: the concentration of the eluent, eluent volume, sample volume, flow-rate and pH. The optimized conditions corresponded to the use of 5 mL of HCl solution 0.8 mol L-1 as an eluent sample volume 50 ml, flow-rate 1.9 mL min-1 and pH 9.0. For the determination of metals by the procedure, the samples after pH adjustment were percolated with the aid of a peristaltic pump on Sep-Pak C18 cartridge with 1-(2-pyridylazo)-2-naphthol (PAN). The analyte elution was carried out with the passage of the HCl solution in the cartridge for subsequent determination by ICP OES. In these conditions, the detection limit for Cu, Fe, Mn, Ni, Pb and Zn varied between 0.11 to 21 μg L-1 and the limits of quantification from 0.36 to 69 μg L-1, respectively. The relative standard deviation (RSD) for the analytes of this study did not exceed 9%. The effect of possible interfering species on the recovery of the analytes was also investigated. The accuracy of the method was evaluated by analysis of certified reference material (SLEW-3 Estuariene Water Reference Material for Trace Metals) and the proposed method was applied to samples of ground water, drinking water and river water collected in Cachoeira and São Félix cities, Bahia, Brazil. The samples were analyzed by Inductively Coupled Plasma Mass Spectrometry (ICP-MS) as a comparative method do not being found significant differences among these results and the results obtained by the proposed method.

Apresenta-se a comparação de duas metodologias para pré-concentração e determinação de Cd em amostras de águas estuarinas e água de mar. As metodologias comparadas foram a extração líquido-líquido no ponto nuvem e a extração por retenção dos analitos em fase sólida. Em ambos os métodos houve necessidade de formação de complexos de Cd previamente à extração. Dois agentes complexantes foram testados o O-O dietilditiofosfato (DDTP), e 1-(2- tiazolilazo)-2-naftol (TAN). A extração no ponto nuvem foi realizada utilizando o surfactante não iônico octil fenoxipolietoxietanol (Triton X-114) que à temperatura de \'40 graus\'C forma uma fase micelar viscosa de volume reduzido. Após separação das micelas, estas foram dissolvidas em solução de ácido nítrico facilitando a análise por ICP OES. A pré-concentração em fase sólida por retenção dos íons complexados foi realizada colocando-se uma coluna de Amberlite XAD 4 em sistema em fluxo. Foram ajustadas as vazões de carregamento da coluna e eluição de forma a aumentar os fatores de pré-concentração. Os volumes das soluções finais foram de 2 mL de forma a obter resultados em triplicata na análise por ICP OES. A quantificação foi efetuada pelo método das adições de padrão. Os dois procedimentos foram comparados considerando as eficiências relativas de pré-concentração, a facilidade para efetuar os procedimentos e a percentagem de recuperação das medidas / Two methodologies for determination of Cd in estuarine and seawater samples were studied. The methodologies for pre-concentration of analytes by surfactant-mediated cloud point extraction and solid phase retention in a resin column were compared. In both cases the prior formation of Cd ions complexes with O,O-diethyldithiophosphate (DDTP) and 1-(2-thiazolylazo)-2-naphtol (TAN) was carried out. The Cloud point extraction was attained with the non ionic surfactant ctylphenoxypolyethoxyethanol (Triton X-114) at \'40 graus\'C . The reduced volume of surfactant micelles was easily separated and dissolved using the solution containing nitric acid which facilitate the analysis by ICP OES. The solid phase pre-concentration was performed by retention of the complexed ions in the Amberlite XAD 4 resin column in a flow scheme. The flow-rates for sample loading and elution were adjusted to increase the preconcentration factor. The final volumes collected of 2 mL were further analyzed in triplicate by ICP OES. Quantification was performed by the standard addition method. Both pre-concentration procedures were compared considering the relative efficiencies, the complexity of procedures and recovery percent of results

Apresenta-se a comparação de duas metodologias para pré-concentração e determinação de Cd em amostras de águas estuarinas e água de mar. As metodologias comparadas foram a extração líquido-líquido no ponto nuvem e a extração por retenção dos analitos em fase sólida. Em ambos os métodos houve necessidade de formação de complexos de Cd previamente à extração. Dois agentes complexantes foram testados o O-O dietilditiofosfato (DDTP), e 1-(2- tiazolilazo)-2-naftol (TAN). A extração no ponto nuvem foi realizada utilizando o surfactante não iônico octil fenoxipolietoxietanol (Triton X-114) que à temperatura de \'40 graus\'C forma uma fase micelar viscosa de volume reduzido. Após separação das micelas, estas foram dissolvidas em solução de ácido nítrico facilitando a análise por ICP OES. A pré-concentração em fase sólida por retenção dos íons complexados foi realizada colocando-se uma coluna de Amberlite XAD 4 em sistema em fluxo. Foram ajustadas as vazões de carregamento da coluna e eluição de forma a aumentar os fatores de pré-concentração. Os volumes das soluções finais foram de 2 mL de forma a obter resultados em triplicata na análise por ICP OES. A quantificação foi efetuada pelo método das adições de padrão. Os dois procedimentos foram comparados considerando as eficiências relativas de pré-concentração, a facilidade para efetuar os procedimentos e a percentagem de recuperação das medidas / Two methodologies for determination of Cd in estuarine and seawater samples were studied. The methodologies for pre-concentration of analytes by surfactant-mediated cloud point extraction and solid phase retention in a resin column were compared. In both cases the prior formation of Cd ions complexes with O,O-diethyldithiophosphate (DDTP) and 1-(2-thiazolylazo)-2-naphtol (TAN) was carried out. The Cloud point extraction was attained with the non ionic surfactant ctylphenoxypolyethoxyethanol (Triton X-114) at \'40 graus\'C . The reduced volume of surfactant micelles was easily separated and dissolved using the solution containing nitric acid which facilitate the analysis by ICP OES. The solid phase pre-concentration was performed by retention of the complexed ions in the Amberlite XAD 4 resin column in a flow scheme. The flow-rates for sample loading and elution were adjusted to increase the preconcentration factor. The final volumes collected of 2 mL were further analyzed in triplicate by ICP OES. Quantification was performed by the standard addition method. Both pre-concentration procedures were compared considering the relative efficiencies, the complexity of procedures and recovery percent of results