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This study investigates the interactions between dissolved trace metals and plastic debris under controlled laboratory conditions by using polyethylene pellets as a model plastic particle. Specifically, the study compared virgin pellets sourced from a local moulding plant with those collected from local beaches and subjected to aging, attrition and deposition of extraneous material. Pellets collected from the coastline of Southwest England were mainly polyethylene according to Fourier transform infra-red spectroscopy (FTIR), although occasional polypropylene pellets were present. Additionally, FTIR was used to identify the extent of degradation of pellets according to a photo-oxidation index derived from the relative magnitudes of specific absorbance peaks, and suggests pellet colour may give an indication of polymer degradation. Acid extractions of pellets collected from the coastline of Southwest England yielded metal concentrations ranging from low ng g-1 for metals such as Cd, Ni and Cr, to 7.7, 10.3 and 290 g g-1 for Cu Pb and Zn, respectively, while Al, Fe and Mn were present on beached pellets at concentrations of up to 171, 314 and 308 g g-1, respectively. Metal concentrations exhibited a high degree of inter- and intra-site variability. Correlation of metal concentrations with the photo-oxidation index indicates that pellet age is not a reliable indicator of metal concentrations. Batch experiments where metals (Cd, Co, Cr, Cu, Ni, Pb, Zn) were added to suspensions of pellets in seawater and estuarine water were performed in order to understand the extent and rates of trace metal adsorption to pellets. Langmuir modelling of adsorption isotherms in seawater indicated a range of maximum values for the accumulation of trace metals on beached pellets from 10 ng g-1 to 720 ng g-1 for Cd and Pb, respectively, in seawater spiked with 5 g L-1 of each trace metal. Langmuir constants for these relationships ranged from 0.140 (Cd) to 2.67 (Ni) mL g-1. Differences between trace metal affinities for pellets collected from the environment (beached) and those obtained directly from a plastics processing facility (virgin) were also identified. Adsorption maxima for virgin pellets ranged from < 1 ng g-1 (Cd) to 300 ng g-1 (Cr) with corresponding, respective Langmuir constants of 0.413 and 0.127 mL g-1. Adsorption of trace metals to beached pellets exceeds that to virgin pellets owing to the development of viable surface sites by photo-oxidation, biofouling and deposition of fine sediment particles on the former during exposure to environmental conditions. Adsorption kinetics were modelled successfully using a pseudo first-order reversible model. Chemical response times derived from kinetic constants ranged from 1.5 – 12 h for beached pellets and 0.2 to 4.5 h for virgin pellets, and were generally lower in seawater than in river water. Applying a similar batch approach to a system simulating an estuarine salinity gradient, the controlling effects of ionic strength and pH on the adsorption of trace metals to pellets were identified. Partitioning of Cd, Co and Ni exhibited inverse relationships with salinity, with partition coefficients (KD) decreasing from values of the order 101 to 10-1 or 10-2 mL g-1 (for beached pellets) as salinity is increased from < 0.05 to 33. Chromium exhibited contrasting behaviour within the estuarine gradient, with partitioning increasing with salinity, while Pb appears to be independent of salinity within this system. Chemical modelling was used to explain the results in context of changes in trace metal speciation which occur through the estuarine gradient. The bioaccessibility of metals on beached pellets to avian species was determined using an in vitro approach. Metal bioaccessibility in a simulated avian gastric environment comprising 10 g L-1 pepsin, 0.1 M NaCl and HCl at pH 2.8 indicated metals on pellets are labile (bioaccessibility ranges from < 10 % (Cr) to > 80 % (Mn)) and may be released readily within the digestive tract. Dissolution kinetics were modelled using the Noyes-Whitney equation, from which rate constants were determined in the range 3.1 x10-4 (Cr) to 8.7 x10-1 %-1 h-1 (Mn). This study has shown, for the first time, that plastic pellets have the potential to accumulate and transport trace metals in the marine environment. Furthermore, metal accumulation on plastic pellets is controlled by estuarine master variables such that conditions which favour or limit adsorption can be defined. Pellets present a previously unreported vector for the transport of metals in the environment, and have the potential to convey metals to organisms upon ingestion. The findings of this thesis have implications for interactions between metals and plastics more generally in the marine environment.

None

This thesis explains a method based on the homogenisation of zeta potential charges on carbon supports for the production of hierarchical structured zeolitic composites. The modification of carbons’ surface chemistry allowed zeolite particles to be fixed to the support by electrostatic interactions. In order to achieve this, the size reduction of zeolite particles was carried out by two different methods: a) ball milling and b) a synthetic route to produce zeolite colloidal dispersions. Also, the seeding method, based on hydrothermal growth was compared. The prepared materials in this work were designed to be used in the sorption of cations, and to allow vitrification and thereby reduce the final adsorbent volume. Results showed that a large pollutant amount can be trapped using a lower volume of material reducing costs and final waste disposal. The zeolites used in this work were selected based on their low density framework and low Si/Al ratio. Synthetic zeolites A, Y and clinoptilolite were successfully produced. Natural clinoptilolite was also utilised in this work. Also, zeolite A was produced at nanometre scale following the clear solutions method. All materials were successfully incorporated onto supports to produce multimodal porosity materials. The hierarchical modification of natural clinoptilolite, following a straightforward and nonexpensive methodology, is one the most significant contributions of this work. Carbons are used as supports due to their high surface area, they can be obtained from low-cost sources such as agroindustrial wastes and carbons allow volume reduction if materials are vitrified at high temperatures. In this work, carbons were produced from corn cob and husk, sugar cane bagasse, cherry stones, date stones and hazelnut shells. The prepared composite materials were tested in the removal of toxic ions from water solutions: cobalt, copper and caesium ions were effectively removed from aqueous media. Adsorption experiments showed that the distribution of supported zeolite particles improved their uptake efficiency and capacity. The kinetic studies revealed an enhanced rate constant for carbon-zeolites composites in comparison with pure zeolites. Diffusivity results suggested that mass transfer characteristics are modified by using hierarchical porous materials; results showed that particle size or support nature can modify diffusion resistances, reducing intraparticle diffusion and accelerating the overall kinetic processes. Adsorption equilibrium data was correlated using Langmuir and Freundlich models.

This work deals with the development of a new label-free detection technique called Pulsed Streaming Potential (PSP). Its novelty relies on the adaptation of a classical electrokinetic phenomenon (streaming potential) into a tool which can evaluate molecular interplay in label-free fashion. Implementation of PSP to microfluidic platforms allowed the label-free sensing of binding events to plastic (modified and unmodified) surfaces. It was demonstrated the use of real time PSP in plastic microfluidic platforms for determination of kinetic parameters of the interaction of proteins and plastic surfaces. Moreover, initial change of PSP after adsorption of proteins showed to be proportional to the bulk concentration of proteins and it was used for quantification of Lysozyme in the nanomolar range. Several approaches were studied to manipulate the surface of microfluidic channels in order to improve selectivity of PSP through reduction of non-specific adsorption. These approaches included the fabrication of composite surface of polyacrilic acid (PAA) and polyethylene glycol acrylate (PEGA) on cyclic olefin copolymer microchannels, as well as adsorption of nanospheres on COC-PEGA channels.

Various concentrations of ferrous and ferric iron solutions were held at room temperature for 60 min before they were assayed for ferrous iron, which may be unstable due to oxidation. The ferrous and ferric solutions (in pH 2 HCl) were maintained as such for 60 min without the use of chelators. There was no significant oxidation of ferrous iron. Also, four different levels of each ferrous and ferric iron were injected into proximal duodenal loops of rat intestine and uptake was determined at four different time intervals. Two iron-replete rats were assigned to each of the treatments. The in situ experiments showed that iron was taken up rapidly from pH 2.0 solutions of ferrous and ferric iron. Maximum amount of iron was taken up in the first 10 min. Uptake of ferrous iron was significantly greater (p < 0.05) than uptake of ferric iron, and there were significant differences in total uptake among the four iron levels used. Uptake, absorption, and adsorption kinetics of both ferrous and ferric iron were determined in situ for both iron-replete and iron-deficient rats. Deficiency caused greater uptake and absorption, confirming a biological adaptation of these processes. Both uptake and absorption were greater for ferrous than for ferric iron and were possibly taken up by different pathways or by a ferrous-ferric pathway with preference for ferrous. Uptake and absorption kinetics were biphasic for both ferrous and ferric iron. The first phase demonstrated saturation kinetics and was followed by a nonsaturable phase at higher concentrations of luminal iron. Iron deficiency altered the uptake and absorption kinetics of ferrous and ferric iron, but not always in a similar manner, suggesting that ferrous and ferric iron were each taken up by a separate pathway. Indications were that enhanced absorption during deficiency was largely due to adaptation of ferric uptake. Iron adsorption was directly proportional to luminal iron concentration, but it was greater for ferric than for ferrous, possibly due to charge interactions. Iron deficiency caused increased adsorption of both ferrous and ferric iron, supporting the notion that adsorption acts to maintain iron in a form available for uptake.

Os resíduos sólidos da indústria coureira são produzidos em diferentes etapas de limpeza, classificação e ajuste da espessura do couro, e são classificados como perigosos quando gerados nas etapas posteriores ao curtimento com cromo. Os resíduos que já passaram pela etapa de curtimento apresentam elevada estabilidade, não sendo facilmente degradados. Além disso, nas etapas do acabamento molhado do couro, em especial no tingimento, corantes são utilizados para conferir cor aos artigos. Devido à necessidade de utilização de água e corantes em excesso, são gerados, nessas etapas, efluentes coloridos. Esses efluentes possuem quantidades elevadas de substâncias solúveis e coloridas que, devido ao seu potencial recalcitrante, não são facilmente removidas em sistemas convencionais de tratamento de efluentes. Neste trabalho, é apresentada uma nova proposta para o uso dos resíduos sólidos da indústria coureira antes de seu destino final, possibilitando assim uma sobrevida a esses resíduos como adsorventes alternativos de substâncias presentes em efluentes industriais do processamento do couro, em especial, os corantes oriundos das operações de acabamento molhado, com perspectivas ao reuso dos efluentes. Os efluentes oriundos da etapa de acabamento molhado de couro em escala piloto foram caracterizados. Assim, soluções aquosas sintéticas no intervalo de concentrações de corantes de efluentes foram preparadas e foi avaliada a capacidade de adsorção de dois tipos de resíduos de couro (curtido ao cromo e vegetal) em diferentes valores de pH. As isotermas de adsorção e cinética dos corantes Amarelo Ácido 194, Vermelho Ácido 357 e Preto Ácido 210 foram obtidos para os resíduos de couro curtido ao cromo no pH ideal de adsorção (entre 2 e 3). Além disso, a remoção do corante presente em efluente de tingimento (obtido em escala piloto) foi otimizada utilizando técnicas sequenciais de planejamento de experimentos. As isotermas apresentaram diferentes comportamentos, sendo do tipo C1, H2 e H3/L3 para os corantes Amarelo 194, Vermelho 357 e Preto 210, respectivamente. Os estudos dos mecanismos de transferência de massa demonstraram que a adsorção do corante Amarelo 194 é controlada pela transferência de massa na camada limite, enquanto que para os corantes Vermelho 357 e Preto 210 também foi observada a difusão no interior da partícula. Para esses dois últimos corantes, as difusividades foram da ordem de 10-9 e 10-11 m2 min-1. Os dados termodinâmicos, associados a análises instrumentais, confirmaram a natureza de adsorção por interações entre os grupos SO3 - e NO2 - dos corantes com os grupos NH(n) + do couro. Para a remoção do corante Vermelho 357 de efluentes de tingimento, uma região de ótimo foi observada para capacidade de adsorção no equilíbrio, correspondente ao pH 3,0 e temperatura entre 16 e 18 °C, sendo obsevado aproximadamente 74 mg g-1 para a concentração de 6,0 g L-1 de adsorvente. Entretanto, na região de estudo não foi observado região de ótimo para a remoção, sendo que para isso seria necessário um deslocamento no planejamento para pH inferiores a 3 e temperaturas superiores a 35 °C, o que de certa forma é inviável. Observouse que a máxima remoção em pH 3 e 35 °C foi de 75 %. O processo de remoção do corante por adsorção foi capaz ainda de reduzir a toxicidade do efluente em cerca de 90 %. / The solid wastes from the tannery industry are produced in different steps of cleaning, sorting and adjusting the thickness of the leather, and they are classified as hazardous waste when they are produced after chrome tanning. The tanned leather wastes present high stability and are not easily degraded. Moreover, in the wet leather finish, particularly during the dyeing process, dyes are used to color the items. Due to the need of using water and dye in excess, colored effluents are generated in these steps. These effluents have high amounts of soluble and colored substances that, due to their recalcitrant potential, are not easily treated in conventional eflluent treatment systems. In this research, a new proposal for the use of solid waste in the leather industry before its final destination is presented, which enables the reuse of these wastes as alternative adsorbents of substances in industrial effluents from the leather processing, particularly dyes derived from wet finishing operations, with the aim of reusing the wastewater. The effluents from the wet leather finish steps in a pilot scale were characterized. Thus, aqueous synthetic solutions in the concentration range of effluent dyes were prepared and the adsorption capacity of two types of leather waste (chrome tanned and vegetable leather) was evaluated at different pH values. Adsorption isotherms and kinetics of Acid Yellow 194, Acid Red 357 and Acid Black 210 dyes were obtained for chrome tanned leather waste in optimal adsorption pH (between 2 and 3). Furthermore, the removal of the dyes in deing wastewater (obtained in a pilot scale) was optimized by using sequential experimental design techniques. The isotherms presented different results: C1, H2 and H3/L3 types for the Yellow 194, Red 357 and Black 210 dyes, respectively. Studies on the mechanisms of mass transfer have shown that the adsorption of the Yellow 194 dye is controlled by mass transfer in the boundary layer, whereas in Red 357 and Black 210 dyes a diffusion was also observed inside the particle. For these last two dyes, diffusivities were 10-9 and 10-11 m2 min-1. The thermodynamic data, associated with instrumental analysis, confirmed the nature of adsorption by interactions between the NO2 - and SO3 - groups of the dyes with the NHn + groups of the leather. For removing the Red 357 dye in dyeing effluents, an optimum region was observed for the adsorption capacity in equilibrium, which corresponds to pH 3.0 to 3.2 and temperature between 16 and 18 °C, with about 74 mg g-1 for the concentration of 6.0 g L-1 adsorbent. However, in the study region an optimum region for the removal was not observed, and this would require a shift in planning for pH below 3 and temperatures above 35 °C, which is somewhat impractical. It was observed that the maximum removal at pH 3 and 35 °C was 75 %. The removing process the dye by adsorption was also able to reduce the toxicity of the effluent by about 90 %.

Os resíduos sólidos da indústria coureira são produzidos em diferentes etapas de limpeza, classificação e ajuste da espessura do couro, e são classificados como perigosos quando gerados nas etapas posteriores ao curtimento com cromo. Os resíduos que já passaram pela etapa de curtimento apresentam elevada estabilidade, não sendo facilmente degradados. Além disso, nas etapas do acabamento molhado do couro, em especial no tingimento, corantes são utilizados para conferir cor aos artigos. Devido à necessidade de utilização de água e corantes em excesso, são gerados, nessas etapas, efluentes coloridos. Esses efluentes possuem quantidades elevadas de substâncias solúveis e coloridas que, devido ao seu potencial recalcitrante, não são facilmente removidas em sistemas convencionais de tratamento de efluentes. Neste trabalho, é apresentada uma nova proposta para o uso dos resíduos sólidos da indústria coureira antes de seu destino final, possibilitando assim uma sobrevida a esses resíduos como adsorventes alternativos de substâncias presentes em efluentes industriais do processamento do couro, em especial, os corantes oriundos das operações de acabamento molhado, com perspectivas ao reuso dos efluentes. Os efluentes oriundos da etapa de acabamento molhado de couro em escala piloto foram caracterizados. Assim, soluções aquosas sintéticas no intervalo de concentrações de corantes de efluentes foram preparadas e foi avaliada a capacidade de adsorção de dois tipos de resíduos de couro (curtido ao cromo e vegetal) em diferentes valores de pH. As isotermas de adsorção e cinética dos corantes Amarelo Ácido 194, Vermelho Ácido 357 e Preto Ácido 210 foram obtidos para os resíduos de couro curtido ao cromo no pH ideal de adsorção (entre 2 e 3). Além disso, a remoção do corante presente em efluente de tingimento (obtido em escala piloto) foi otimizada utilizando técnicas sequenciais de planejamento de experimentos. As isotermas apresentaram diferentes comportamentos, sendo do tipo C1, H2 e H3/L3 para os corantes Amarelo 194, Vermelho 357 e Preto 210, respectivamente. Os estudos dos mecanismos de transferência de massa demonstraram que a adsorção do corante Amarelo 194 é controlada pela transferência de massa na camada limite, enquanto que para os corantes Vermelho 357 e Preto 210 também foi observada a difusão no interior da partícula. Para esses dois últimos corantes, as difusividades foram da ordem de 10-9 e 10-11 m2 min-1. Os dados termodinâmicos, associados a análises instrumentais, confirmaram a natureza de adsorção por interações entre os grupos SO3 - e NO2 - dos corantes com os grupos NH(n) + do couro. Para a remoção do corante Vermelho 357 de efluentes de tingimento, uma região de ótimo foi observada para capacidade de adsorção no equilíbrio, correspondente ao pH 3,0 e temperatura entre 16 e 18 °C, sendo obsevado aproximadamente 74 mg g-1 para a concentração de 6,0 g L-1 de adsorvente. Entretanto, na região de estudo não foi observado região de ótimo para a remoção, sendo que para isso seria necessário um deslocamento no planejamento para pH inferiores a 3 e temperaturas superiores a 35 °C, o que de certa forma é inviável. Observouse que a máxima remoção em pH 3 e 35 °C foi de 75 %. O processo de remoção do corante por adsorção foi capaz ainda de reduzir a toxicidade do efluente em cerca de 90 %. / The solid wastes from the tannery industry are produced in different steps of cleaning, sorting and adjusting the thickness of the leather, and they are classified as hazardous waste when they are produced after chrome tanning. The tanned leather wastes present high stability and are not easily degraded. Moreover, in the wet leather finish, particularly during the dyeing process, dyes are used to color the items. Due to the need of using water and dye in excess, colored effluents are generated in these steps. These effluents have high amounts of soluble and colored substances that, due to their recalcitrant potential, are not easily treated in conventional eflluent treatment systems. In this research, a new proposal for the use of solid waste in the leather industry before its final destination is presented, which enables the reuse of these wastes as alternative adsorbents of substances in industrial effluents from the leather processing, particularly dyes derived from wet finishing operations, with the aim of reusing the wastewater. The effluents from the wet leather finish steps in a pilot scale were characterized. Thus, aqueous synthetic solutions in the concentration range of effluent dyes were prepared and the adsorption capacity of two types of leather waste (chrome tanned and vegetable leather) was evaluated at different pH values. Adsorption isotherms and kinetics of Acid Yellow 194, Acid Red 357 and Acid Black 210 dyes were obtained for chrome tanned leather waste in optimal adsorption pH (between 2 and 3). Furthermore, the removal of the dyes in deing wastewater (obtained in a pilot scale) was optimized by using sequential experimental design techniques. The isotherms presented different results: C1, H2 and H3/L3 types for the Yellow 194, Red 357 and Black 210 dyes, respectively. Studies on the mechanisms of mass transfer have shown that the adsorption of the Yellow 194 dye is controlled by mass transfer in the boundary layer, whereas in Red 357 and Black 210 dyes a diffusion was also observed inside the particle. For these last two dyes, diffusivities were 10-9 and 10-11 m2 min-1. The thermodynamic data, associated with instrumental analysis, confirmed the nature of adsorption by interactions between the NO2 - and SO3 - groups of the dyes with the NHn + groups of the leather. For removing the Red 357 dye in dyeing effluents, an optimum region was observed for the adsorption capacity in equilibrium, which corresponds to pH 3.0 to 3.2 and temperature between 16 and 18 °C, with about 74 mg g-1 for the concentration of 6.0 g L-1 adsorbent. However, in the study region an optimum region for the removal was not observed, and this would require a shift in planning for pH below 3 and temperatures above 35 °C, which is somewhat impractical. It was observed that the maximum removal at pH 3 and 35 °C was 75 %. The removing process the dye by adsorption was also able to reduce the toxicity of the effluent by about 90 %.

Os resíduos sólidos da indústria coureira são produzidos em diferentes etapas de limpeza, classificação e ajuste da espessura do couro, e são classificados como perigosos quando gerados nas etapas posteriores ao curtimento com cromo. Os resíduos que já passaram pela etapa de curtimento apresentam elevada estabilidade, não sendo facilmente degradados. Além disso, nas etapas do acabamento molhado do couro, em especial no tingimento, corantes são utilizados para conferir cor aos artigos. Devido à necessidade de utilização de água e corantes em excesso, são gerados, nessas etapas, efluentes coloridos. Esses efluentes possuem quantidades elevadas de substâncias solúveis e coloridas que, devido ao seu potencial recalcitrante, não são facilmente removidas em sistemas convencionais de tratamento de efluentes. Neste trabalho, é apresentada uma nova proposta para o uso dos resíduos sólidos da indústria coureira antes de seu destino final, possibilitando assim uma sobrevida a esses resíduos como adsorventes alternativos de substâncias presentes em efluentes industriais do processamento do couro, em especial, os corantes oriundos das operações de acabamento molhado, com perspectivas ao reuso dos efluentes. Os efluentes oriundos da etapa de acabamento molhado de couro em escala piloto foram caracterizados. Assim, soluções aquosas sintéticas no intervalo de concentrações de corantes de efluentes foram preparadas e foi avaliada a capacidade de adsorção de dois tipos de resíduos de couro (curtido ao cromo e vegetal) em diferentes valores de pH. As isotermas de adsorção e cinética dos corantes Amarelo Ácido 194, Vermelho Ácido 357 e Preto Ácido 210 foram obtidos para os resíduos de couro curtido ao cromo no pH ideal de adsorção (entre 2 e 3). Além disso, a remoção do corante presente em efluente de tingimento (obtido em escala piloto) foi otimizada utilizando técnicas sequenciais de planejamento de experimentos. As isotermas apresentaram diferentes comportamentos, sendo do tipo C1, H2 e H3/L3 para os corantes Amarelo 194, Vermelho 357 e Preto 210, respectivamente. Os estudos dos mecanismos de transferência de massa demonstraram que a adsorção do corante Amarelo 194 é controlada pela transferência de massa na camada limite, enquanto que para os corantes Vermelho 357 e Preto 210 também foi observada a difusão no interior da partícula. Para esses dois últimos corantes, as difusividades foram da ordem de 10-9 e 10-11 m2 min-1. Os dados termodinâmicos, associados a análises instrumentais, confirmaram a natureza de adsorção por interações entre os grupos SO3 - e NO2 - dos corantes com os grupos NH(n) + do couro. Para a remoção do corante Vermelho 357 de efluentes de tingimento, uma região de ótimo foi observada para capacidade de adsorção no equilíbrio, correspondente ao pH 3,0 e temperatura entre 16 e 18 °C, sendo obsevado aproximadamente 74 mg g-1 para a concentração de 6,0 g L-1 de adsorvente. Entretanto, na região de estudo não foi observado região de ótimo para a remoção, sendo que para isso seria necessário um deslocamento no planejamento para pH inferiores a 3 e temperaturas superiores a 35 °C, o que de certa forma é inviável. Observouse que a máxima remoção em pH 3 e 35 °C foi de 75 %. O processo de remoção do corante por adsorção foi capaz ainda de reduzir a toxicidade do efluente em cerca de 90 %. / The solid wastes from the tannery industry are produced in different steps of cleaning, sorting and adjusting the thickness of the leather, and they are classified as hazardous waste when they are produced after chrome tanning. The tanned leather wastes present high stability and are not easily degraded. Moreover, in the wet leather finish, particularly during the dyeing process, dyes are used to color the items. Due to the need of using water and dye in excess, colored effluents are generated in these steps. These effluents have high amounts of soluble and colored substances that, due to their recalcitrant potential, are not easily treated in conventional eflluent treatment systems. In this research, a new proposal for the use of solid waste in the leather industry before its final destination is presented, which enables the reuse of these wastes as alternative adsorbents of substances in industrial effluents from the leather processing, particularly dyes derived from wet finishing operations, with the aim of reusing the wastewater. The effluents from the wet leather finish steps in a pilot scale were characterized. Thus, aqueous synthetic solutions in the concentration range of effluent dyes were prepared and the adsorption capacity of two types of leather waste (chrome tanned and vegetable leather) was evaluated at different pH values. Adsorption isotherms and kinetics of Acid Yellow 194, Acid Red 357 and Acid Black 210 dyes were obtained for chrome tanned leather waste in optimal adsorption pH (between 2 and 3). Furthermore, the removal of the dyes in deing wastewater (obtained in a pilot scale) was optimized by using sequential experimental design techniques. The isotherms presented different results: C1, H2 and H3/L3 types for the Yellow 194, Red 357 and Black 210 dyes, respectively. Studies on the mechanisms of mass transfer have shown that the adsorption of the Yellow 194 dye is controlled by mass transfer in the boundary layer, whereas in Red 357 and Black 210 dyes a diffusion was also observed inside the particle. For these last two dyes, diffusivities were 10-9 and 10-11 m2 min-1. The thermodynamic data, associated with instrumental analysis, confirmed the nature of adsorption by interactions between the NO2 - and SO3 - groups of the dyes with the NHn + groups of the leather. For removing the Red 357 dye in dyeing effluents, an optimum region was observed for the adsorption capacity in equilibrium, which corresponds to pH 3.0 to 3.2 and temperature between 16 and 18 °C, with about 74 mg g-1 for the concentration of 6.0 g L-1 adsorbent. However, in the study region an optimum region for the removal was not observed, and this would require a shift in planning for pH below 3 and temperatures above 35 °C, which is somewhat impractical. It was observed that the maximum removal at pH 3 and 35 °C was 75 %. The removing process the dye by adsorption was also able to reduce the toxicity of the effluent by about 90 %.

Orientadores: Aline Carvalho da Costa, José Geraldo da Cruz Pradella / Dissertação (mestrado) - Universidade Estadual de Campinas, Faculdade de Engenharia Química / Made available in DSpace on 2018-08-24T06:05:42Z (GMT). No. of bitstreams: 1 Machado_DanieleLongo_M.pdf: 2642371 bytes, checksum: 08fe9958b60f1f20bc5bb385ae8820e4 (MD5) Previous issue date: 2013 / Resumo: A hidrólise enzimática de materiais lignocelulósicos compreende uma etapa de adsorção das enzimas celulases a esse material, e as chamadas isotermas de adsorção são curvas extremamente úteis nesse estudo, pois indicam a forma como o soluto (adsorbato) adsorverá no adsorvente; dão uma estimativa da quantidade máxima de soluto que o adsorvente adsorverá, entre outras características importantes. São empregadas também para a obtenção de condições mais favoráveis e eficientes na conversão da biomassa a açúcares fermentescíveis. Assim, para melhor entendimento de como o processo da adsorção enzimática interfere nos rendimentos da hidrólise enzimática da celulose, este trabalho abordou estudos específicos, tais como, a determinação da cinética e dos parâmetros das isotermas de adsorção das enzimas do complexo celulolítico sobre diferentes biomassas. Trabalhou-se com o bagaço de cana-de-açúcar pré-tratado hidrotérmico (BH) que apresentou 31,97% de lignina em sua composição e organossolve (BO), com 4,42% de lignina, e também com Avicel e com um isolado de lignina (IL). Os experimentos de cinética e isoterma de adsorção foram realizados em duplicata com volume reacional de 15 mL contendo tãmpão citrato de sódio 50 mM pH 4.8 complementado com with 0.02% de azida sódica por grrama de substrato onde a biomassa foi adicionada. Nos ensaios de cinética, os fracos foram incubados em um shaker (Marconi AM-832) a 50ºC e 4ºC, onde a agitação variou de 40 a 250 rpm. Foram recolhidas amostras dos frascos em tempos pré-determinados e centrifugadas por 15 min a 4,000 rpm para remoção dos materiais insolúveis. O teor de proteína do sobrenadante foi determinado usando o método de Bradford. As isotermas de adsorção da celulase para as biomassas foram conduzidas pela variação da quantidade proteica da enzima celulase (0,1 ¿ 4,5 mg/mL). Os dados experimentais foram estimados pela isoterma de adsorção de Langmuir usando o software OriginPro8.0. Os parâmetros Emax e Kp obtidos pelo ajuste dos dados experimentais mostraram-se diferentes para os diferentes materiais. Uma maior capacidade de adsorção (36,93 mg celulase/g de substrato) e, consequentemente, uma afinidade maior da enzima celulase pelo bagaço pré-tratado foi observada para o pré-tratamento hidrotérmico, pois a celulase, além de adsorver na celulose, também adsorve na lignina, em menor extensão. Os dados obtidos da isoterma de adsorção da celulase sobre o IL confirmam a adsorção improdutiva da enzima na lignina (Emax= 11,92 mg/g) e mostram como esses estudos da adsorção das enzimas em IL são importantes, porque se torna possível distinguir a adsorção a porções da celulose e frações da lignina. A agitação exerceu influência significativa no fenômeno de adsorção, onde o aumento da agitação até 150 rpm melhorou a mistura entre as enzimas e o substratos, porém, a partir de 200 rpm não foram observadas mudanças significativas nos perfis de enzima adsorvida. Palavras-chaves: Lignocelulose, cinética de adsorção, isoterma de Langmuir, hidrólise enzimática / Abstract: The enzymatic hydrolysis of lignocellulosic biomass involves one step of adsorption of cellulase enzymes on this material, and the adsorption isotherms are curves extremely useful for this research, because they show how the solute (adsorbate) will adsorb on the adsorbent; give an estimate of what is highest quantity of solute adsorbed by the adsorbent, among other information. They are also used to attain more favorable and efficient conditions in the conversion of biomass into fermentable sugars. Therefore, for a better understanding of how the enzymatic adsorption process interferes in the enzymatic hydrolysis of cellulose yields, this study has proposed specific studies, such as the determination of the kinetics and parameters of adsorption isotherms of enzymes from cellulolityc complex on different biomasses. Sugarcane bagasse hydrothermal pretreated (BH), which presented 31.97% (w/w) of lignin in its composition, and the organosolv (BO), with 4.42% (w/w) of lignin, were evaluated, as well as Avicel and an isolated lignin (IL). The adsorption kinetics and isotherm experiments assays were performed in duplicate with reaction volume of 15 mL of sodium citrate buffer 50 mM pH 4.8 supplemented with 0.02% sodium azide per gram of substrate to which biomass was added. The adsorption kinetics assays the flasks were incubated in shaker (Marconi AM-832) at 50ºC and 4ºC where the stirring ranged from 40 to 250 rpm. Flasks were withdrawn at different time intervals and centrifuged repeatedly for 15 min in a centrifuge at 4,000 rpm to remove insoluble materials. The protein content of the supernatant was determined using Bradford method (Bradford, 1976). Cellulase adsorption isotherm on biomasses was conducted by varying the amount of cellulase protein (0.1¿4.5 mg/mL). The experimental data were fit to the Langmuir adsorption isotherm using the software OriginPro 8.0. The parameters Emax and Kp estimated by experimental data adjustment showed different values to the different materials. The highest adsorption capacity (36.93 mg of cellulase/ g of substrate) and, consequently, the highest affinity of the cellulase enzyme for the pretreated bagasse was found for the hydrothermal pretreated bagasse, as cellulase, besides adsorbing on cellulose, also adsorbs on lignin to a lesser extent. The cellulase adsorption on IL data confirms the unproductive adsorption of the enzyme on lignin (Emax = 11.92 mg/g) and shows how these adsorption studies of enzymes in IL are relevant, because it becomes feasible to distinguish the adsorption on portions of cellulose and on lignin fractions. Stirring had significant influence on the adsorption phenomenon, with the increase in stirring up to 150 rpm improving the mixture of enzymes and substrate; however, over 200 rpm stirring influence was not significant. Key-words: Lignocellulose, adsorption kinetics, Langmuir isotherm, enzymatic hydrolysis / Mestrado / Desenvolvimento de Processos Químicos / Mestra em Engenharia Química