Aluminium recycling requires 95% less energy than primary production with no loss of quality. The Black Dross (BD) produced during secondary aluminium production contains high amounts of water-soluble compounds, therefore it is considered as a toxic waste. In the present work, salt removal from BD by thermal treatment has been investigated in laboratory scale. The optimum conditions for treatment were established, i.e., temperature, gas flow rate, holding time, rotation rate, and sample size. The overall degree of chloride removal was established to increase as a function of time and temperature. Even Pretreated Black Dross (PBD) was evaluated as a possible raw material for the production of a calcium aluminate-based ladle-fluxing agent to be used in the steel industry. The effects of different process parameters on the properties of the produced flux were experimentally investigated, i.e. CaO/Al2O3 ratio, temperature, holding time, and cooling media. The utilization of PBD as the alumina source during the production of a calcium aluminate fluxing agent shows promising results. The iron/steel industry is responsible for 9% of anthropogenic energy and process CO2 emissions. It is believed that the only way to a long-term reduction of the CO2 emissions from the iron/steel industry is commercialization of alternative processes such as Direct Reduction (DR) of iron oxide. Detailed knowledge of the kinetics of the reduction reactions is, however, a prerequisite for the design and optimization of the DR process. To obtain a better understanding of the reduction kinetics, a model was developed step-by-step, from a single pellet to a fixed bed with many pellets. The equations were solved using the commercial software COMSOL Multiphysics®. The final model considers the reaction rate and mass transfer inside the pellet, as well as the mass transfers and heat transfer in the fixed bed. All the models were verified against experimental results, and where found to describe the results in a satisfying way. / <p>QC 20161128</p>

O reprocessamento do elemento combustível constitui uma das etapas do ciclo do combustível e tem por objetivo separar U 235, U238 e Pu239 dos produtos de fissão contidos no elemento combustível queimado para reutilizá -los na fabricação de novos elementos combustíveis. No Brasil, o desenvolvimento do reprocessamento teve início nos anos 70 com a implantação de uma planta piloto de reprocessamento, no Instituto de Pesquisas Energéticas e Nucleares Comissão Nacional de Energia Nuclear/São Paulo (I PEN-CNEN/SP), dando origem à uma instalação, em escala de laboratório, que operou até o início da década de 90. Parte dos rejeitos radioativos, produzidos principalmente a partir dos laboratórios analíticos está armazenados à espera de tratamento no Labora tório de Gestão de Rejeitos do IPEN-CNEN/SP, e são constituído pela mistura de fases aquosa e orgânica. Por conter compostos orgânicos, esses rejeitos não podem se solidificados diretamente com cimento, necessitando para isso, de tratamento prévio para torná-los compatíveis. Desta forma, o objetivo deste trabalho foi desenvolver uma metodologia de biodegradação dos compostos orgânicos que compõem os rejeitos radioativos líquidos orgânicos (RRLO) para que os mesmos possam ser posteriormente imobilizados em c imento. O trabalho foi dividido em três etapas, a de caracterização dos RRLO, obtenção das comunidades microbianas (da mina de urânio de Poços de Caldas e do estuário de São Sebastião) e realização de ensaios de biodegradação dos RRLO. A partir da caracterização dos rejeitos, a biodegradação do TBP e acetato de etila foram monitoradas. Os resultados mostraram que as comunidades bacterianas selecionadas foram eficientes para a degradação dos rejeitos radioativos líquidos orgânicos. Ao final dos experimentos os níveis biodegradação foram de 66% para o acetato de etila e 70% para o TBP. / The research and development program in reproces sing of low burn-up spent fuel elements began in Brazil in 70s, originating the lab -scale hot cell, known as CELESTE located at Nuclear and Energy Research Institute, IPEN - CNEN/SP. The program was ended at the beginning of 90s, and the laboratory was c losed down. Part of the radioactive waste generated mainly from the analytical laboratories is stored waiting for treatment at the Waste Management Laboratory, and it is constituted by mixture of aqueous and organic phases. The most widely used technique for the treatment of radioactive liquid wastes is the solidification in cement matrix, due to the low processing costs and compatibility with a wide variety of wastes. However, organics are generally incompatible with cement, interfering with the hydration and setting processes, and requiring pre -treatment with special additives to stabilize or destroy them. The objective of this work can be divided in three parts: i) organic compounds characterization in the radioactive liquid waste; ii) the occurrence of b acterial consortia from Poços de Caldas uranium mine soil and São Sebastião estuary sediments that are able to degrade organic compounds and third, the development of a methodology to biodegrade organic compounds from the radioactive liquid waste aiming th e cementation From the characterization analysis, TBP and ethyl acetate were chosen to be degrade d. The results showed that selected bacterial consortia were efficient for the organic liquid wastes degradation. At the end of the experiments the biodegradat ion level were 66% for ethyl acetate and 70% for the TBP.

O reprocessamento do elemento combustível constitui uma das etapas do ciclo do combustível e tem por objetivo separar U 235, U238 e Pu239 dos produtos de fissão contidos no elemento combustível queimado para reutilizá -los na fabricação de novos elementos combustíveis. No Brasil, o desenvolvimento do reprocessamento teve início nos anos 70 com a implantação de uma planta piloto de reprocessamento, no Instituto de Pesquisas Energéticas e Nucleares Comissão Nacional de Energia Nuclear/São Paulo (I PEN-CNEN/SP), dando origem à uma instalação, em escala de laboratório, que operou até o início da década de 90. Parte dos rejeitos radioativos, produzidos principalmente a partir dos laboratórios analíticos está armazenados à espera de tratamento no Labora tório de Gestão de Rejeitos do IPEN-CNEN/SP, e são constituído pela mistura de fases aquosa e orgânica. Por conter compostos orgânicos, esses rejeitos não podem se solidificados diretamente com cimento, necessitando para isso, de tratamento prévio para torná-los compatíveis. Desta forma, o objetivo deste trabalho foi desenvolver uma metodologia de biodegradação dos compostos orgânicos que compõem os rejeitos radioativos líquidos orgânicos (RRLO) para que os mesmos possam ser posteriormente imobilizados em c imento. O trabalho foi dividido em três etapas, a de caracterização dos RRLO, obtenção das comunidades microbianas (da mina de urânio de Poços de Caldas e do estuário de São Sebastião) e realização de ensaios de biodegradação dos RRLO. A partir da caracterização dos rejeitos, a biodegradação do TBP e acetato de etila foram monitoradas. Os resultados mostraram que as comunidades bacterianas selecionadas foram eficientes para a degradação dos rejeitos radioativos líquidos orgânicos. Ao final dos experimentos os níveis biodegradação foram de 66% para o acetato de etila e 70% para o TBP. / The research and development program in reproces sing of low burn-up spent fuel elements began in Brazil in 70s, originating the lab -scale hot cell, known as CELESTE located at Nuclear and Energy Research Institute, IPEN - CNEN/SP. The program was ended at the beginning of 90s, and the laboratory was c losed down. Part of the radioactive waste generated mainly from the analytical laboratories is stored waiting for treatment at the Waste Management Laboratory, and it is constituted by mixture of aqueous and organic phases. The most widely used technique for the treatment of radioactive liquid wastes is the solidification in cement matrix, due to the low processing costs and compatibility with a wide variety of wastes. However, organics are generally incompatible with cement, interfering with the hydration and setting processes, and requiring pre -treatment with special additives to stabilize or destroy them. The objective of this work can be divided in three parts: i) organic compounds characterization in the radioactive liquid waste; ii) the occurrence of b acterial consortia from Poços de Caldas uranium mine soil and São Sebastião estuary sediments that are able to degrade organic compounds and third, the development of a methodology to biodegrade organic compounds from the radioactive liquid waste aiming th e cementation From the characterization analysis, TBP and ethyl acetate were chosen to be degrade d. The results showed that selected bacterial consortia were efficient for the organic liquid wastes degradation. At the end of the experiments the biodegradat ion level were 66% for ethyl acetate and 70% for the TBP.

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