A presente pesquisa objetivou estudar a remoção dos poluentes presentes em uma água residuária de coqueria, através do processo biológico de nitritação/desnitritação operando um reator de lodo ativado em bateladas seqüenciais em duas etapas sucessivas. Durante a primeira, o reator foi alimentado com um efluente sintético composto por dois poluentes abundantes em despejos de coqueria: nitrogênio amoniacal (500 mg N/L) e fenol (1.000 mg C6H5OH/L). Na segunda, o reator foi alimentado com o despejo gerado na unidade de coqueria de uma indústria siderúrgica integrada. Ao longo da primeira etapa, ao final da fase aeróbia dos 28 ciclos de tratamento, foi possível alcançar eficiências de remoção de N-NH3 superiores a 90% com predominância do N-NO2 - na massa líquida do reator evidenciado pelas relações N-NO2 -/ (N-NO2 - + N-NO3 -) superiores a 86%. O principal mecanismo de inibição das bactérias oxidantes de nitrito (BON) foram concentrações de amônia livre no conteúdo do reator entre 3,2 e 19,5 mg NH3/L. As taxas específicas de nitritação variaram entre 0,03 e 0,11 kg N-NH3/ kg SSV.dia, para temperaturas no conteúdo do reator entre 15 e 34°C. Durante a fase anóxica, o fenol mostrou-se adequado como fonte de carbono para a biomassa desnitritante, desde que as taxas de aplicação volumétricas fossem inferiores a 0,02 kg fenol/m³.hora. Respeitando essa condição, foi possível alcançar: eficiências de remoção de fenol entre 45 e 56%; taxas específicas de remoção de fenol entre 0,03 e 0,09 kg C6H5OH / kg SSV.dia; taxas específicas de desnitritação entre 0,03 e 0,06 kg N-NO2 -/ kg SSV.dia e eficiências de remoção de (N-NO2 - + N-NO3 -) superiores a 95%. Ao longo da fase anóxica foram retiradas amostras do conteúdo do reator para a realização de análises de nitrofenóis (NF). Os resultados acusaram a presença de 2 nitrofenol e 4 nitrofenol em concentrações proporcionais à taxa de aplicação volumétrica do fenol na massa líquida do reator. A presença desses compostos em concentrações inferiores a 0,5 mg/L não causou impacto sobre a desnitritação biológica. As análises realizadas em amostras coletadas ao final da reação anóxica, não acusaram a presença de 2 e 4 NF, demonstrando que esses compostos podem ser biodegradados por uma biomassa bem adaptada ao fenol. A concepção do sistema para tratamento da água residuária de coqueria via nitritação/desnitritação envolveu a operação de dois reatores (principal e reator de polimento) operados em bateladas seqüenciais. As condições de operação do reator principal eram manipuladas para viabilizar o acúmulo de NNO2 - ao final da fase aeróbia e promover a desnitritação durante a fase anóxica, utilizando como fonte de carbono a própria matéria orgânica presente no despejo. Como o sobrenadante do reator principal apresentava concentrações elevadas de N-NO2 -, esse efluente era aplicado no reator de polimento, juntamente com etanol como fonte de carbono para redução do NNO2 -. Ao final da fase aeróbia dos ciclos de tratamento conduzidos no reator principal alcançaram-se: relações NO2 -/ (N-NO2 - + N-NO3 -) superiores a 88%; eficiências de remoções de nitrogênio total superiores a 60%; remoções de N-NH3 superiores a 90%, para valores de pH na massa líquida do reator entre 7,8 e 8,5 e, temperatura entre 23 e 31°C. Tal qual ocorrido durante a primeira etapa da investigação, o principal mecanismo de inibição da atividade das bactérias oxidantes de nitrito foi a toxicidade conferida pelas concentrações de amônia livre (3,7 a 15,7 mg NH3/L) no conteúdo do reator. Durante a fase anóxica, as eficiências de remoção de (N-NO2 - foram limitadas pela disponibilidade de matéria orgânica biodegradável no despejo da coqueria, razões DBO/DQOafluente superiores a 80% resultaram em remoções de N-NO2 - próximas de 100%. Quanto ao reator de polimento, pode-se afirmar que o etanol teve um efeito positivo sobre a remoção de matéria orgânica da água residuária da coqueria, considerando a configuração (dois lodos) utilizada. / The present research aimed to study the coke-oven wastewater treatment over nitritation/denitritation in an activated sludge sequencing batch reactor in two successive phases. During the first one, the reactor was fed with a synthetic effluent composed by two abundant pollutants present in coke-oven wastewaters: total ammonia nitrogen (500 mg TAN.l-1) and phenol (1,000 mg C6H5OH.l-1). During the second phase, the reactor was fed with the wastewater produced in an integrated steel industrys coke-plant. The results of the first phase (28 cycles) showed that was possible to achieve TAN removal efficiencies higher than 90% with NO2 --N predominance in the reactor content, evidenced by the rates NO2 --N/ (NO2 --N + NO3 --N) higher than 86%. The main mechanism of the nitrite oxidizer bacteria (NOB) inhibition was free ammonia concentrations between 3.2 and 19.5 mg NH3.l-1. The specific nitritation rates varied between 0.03 and 0.11 kg TAN. kg VSS-1.d-1, for temperatures between 15 and 34oC. Phenol showed to be suitable as carbon source for denitrifying biomass, once the volumetric application rates were lower than 0.02 kg phenol.m-3.h-1. Obeying this condition, it was possible to achieve: phenol removal efficiencies between 45 and 56%; specific phenol removal rates between 0.03 and 0.09 kg C6H5OH. kg VSS-1.d-1; specific denitritation rates between 0.03 and 0.06 kg NO2 --N . kg VSS-1.d-1 and removal efficiencies of (NO2 --N + NO3 --N) higher than 95%. During the anoxic phase, samples were collected from the reactor content for nitrophenols analyses. The results showed the presence of 2- nitrophenol (2-NP) and 4-nitrophenol (4-NP) in concentrations proportional to phenol volumetric application rate in the reactor liquid mass. The presence of those compounds in concentrations lower than 0.5 mg/L does not cause impact over the biological denitritation. The analyses accomplished in samples collected at the end of the anoxic reaction do not show the presence of 2 and 4-NP, demonstrating that these compounds can be biodegraded by a well-adapted biomass. The arrangement of the system for the treatment of coke-oven wastewater (Phase 02) over nitritation/denitritation involved the operation of two sequencing batch reactors (the main reactor and the polishing one). The operational conditions of the main reactor were manipulated to make feasible the NO2 --N accumulation at the end of the aerobic stage and promote the denitritation using the own organic matter present in the cokeoven wastewater as carbon source. As the supernatant of the main reactor presented high nitrite concentrations, this effluent was conducted to a biological denitrifying polishing reactor with ethanol as carbon source. At the end of the aerobic stage of the treatment cycles conducted in the main reactor, it was achieved: NO2 --N/ (NO2 --N + NO3 --N) higher than 88%; total nitrogen removal efficiencies higher than 60%; ammonia nitrogen removal higher than 90%. As occurred during the first phase of the investigation, the main NOB activity inhibition was the toxicity of the free ammonia concentrations (3.7 to 15.7 mg NH3.l-1) in the reactor content. At the end of anoxic stage, the NO2 --N removal efficiencies were limited by the availability of the biodegradable organic matter in the coke-oven wastewater but BOD/CODinfluent higher than 80% resulted in NO2 --N removals next to 100%. Regarding to the polishing reactor, it can be stated that the ethanol had a positive effect over the organic matter removal of the coke-oven wastewater.

Thesis (Ph. D.)--Rutgers University, 2008. / "Graduate Program in Public Health." Includes bibliographical references.

A presente pesquisa objetivou estudar a remoção dos poluentes presentes em uma água residuária de coqueria, através do processo biológico de nitritação/desnitritação operando um reator de lodo ativado em bateladas seqüenciais em duas etapas sucessivas. Durante a primeira, o reator foi alimentado com um efluente sintético composto por dois poluentes abundantes em despejos de coqueria: nitrogênio amoniacal (500 mg N/L) e fenol (1.000 mg C6H5OH/L). Na segunda, o reator foi alimentado com o despejo gerado na unidade de coqueria de uma indústria siderúrgica integrada. Ao longo da primeira etapa, ao final da fase aeróbia dos 28 ciclos de tratamento, foi possível alcançar eficiências de remoção de N-NH3 superiores a 90% com predominância do N-NO2 - na massa líquida do reator evidenciado pelas relações N-NO2 -/ (N-NO2 - + N-NO3 -) superiores a 86%. O principal mecanismo de inibição das bactérias oxidantes de nitrito (BON) foram concentrações de amônia livre no conteúdo do reator entre 3,2 e 19,5 mg NH3/L. As taxas específicas de nitritação variaram entre 0,03 e 0,11 kg N-NH3/ kg SSV.dia, para temperaturas no conteúdo do reator entre 15 e 34°C. Durante a fase anóxica, o fenol mostrou-se adequado como fonte de carbono para a biomassa desnitritante, desde que as taxas de aplicação volumétricas fossem inferiores a 0,02 kg fenol/m³.hora. Respeitando essa condição, foi possível alcançar: eficiências de remoção de fenol entre 45 e 56%; taxas específicas de remoção de fenol entre 0,03 e 0,09 kg C6H5OH / kg SSV.dia; taxas específicas de desnitritação entre 0,03 e 0,06 kg N-NO2 -/ kg SSV.dia e eficiências de remoção de (N-NO2 - + N-NO3 -) superiores a 95%. Ao longo da fase anóxica foram retiradas amostras do conteúdo do reator para a realização de análises de nitrofenóis (NF). Os resultados acusaram a presença de 2 nitrofenol e 4 nitrofenol em concentrações proporcionais à taxa de aplicação volumétrica do fenol na massa líquida do reator. A presença desses compostos em concentrações inferiores a 0,5 mg/L não causou impacto sobre a desnitritação biológica. As análises realizadas em amostras coletadas ao final da reação anóxica, não acusaram a presença de 2 e 4 NF, demonstrando que esses compostos podem ser biodegradados por uma biomassa bem adaptada ao fenol. A concepção do sistema para tratamento da água residuária de coqueria via nitritação/desnitritação envolveu a operação de dois reatores (principal e reator de polimento) operados em bateladas seqüenciais. As condições de operação do reator principal eram manipuladas para viabilizar o acúmulo de NNO2 - ao final da fase aeróbia e promover a desnitritação durante a fase anóxica, utilizando como fonte de carbono a própria matéria orgânica presente no despejo. Como o sobrenadante do reator principal apresentava concentrações elevadas de N-NO2 -, esse efluente era aplicado no reator de polimento, juntamente com etanol como fonte de carbono para redução do NNO2 -. Ao final da fase aeróbia dos ciclos de tratamento conduzidos no reator principal alcançaram-se: relações NO2 -/ (N-NO2 - + N-NO3 -) superiores a 88%; eficiências de remoções de nitrogênio total superiores a 60%; remoções de N-NH3 superiores a 90%, para valores de pH na massa líquida do reator entre 7,8 e 8,5 e, temperatura entre 23 e 31°C. Tal qual ocorrido durante a primeira etapa da investigação, o principal mecanismo de inibição da atividade das bactérias oxidantes de nitrito foi a toxicidade conferida pelas concentrações de amônia livre (3,7 a 15,7 mg NH3/L) no conteúdo do reator. Durante a fase anóxica, as eficiências de remoção de (N-NO2 - foram limitadas pela disponibilidade de matéria orgânica biodegradável no despejo da coqueria, razões DBO/DQOafluente superiores a 80% resultaram em remoções de N-NO2 - próximas de 100%. Quanto ao reator de polimento, pode-se afirmar que o etanol teve um efeito positivo sobre a remoção de matéria orgânica da água residuária da coqueria, considerando a configuração (dois lodos) utilizada. / The present research aimed to study the coke-oven wastewater treatment over nitritation/denitritation in an activated sludge sequencing batch reactor in two successive phases. During the first one, the reactor was fed with a synthetic effluent composed by two abundant pollutants present in coke-oven wastewaters: total ammonia nitrogen (500 mg TAN.l-1) and phenol (1,000 mg C6H5OH.l-1). During the second phase, the reactor was fed with the wastewater produced in an integrated steel industrys coke-plant. The results of the first phase (28 cycles) showed that was possible to achieve TAN removal efficiencies higher than 90% with NO2 --N predominance in the reactor content, evidenced by the rates NO2 --N/ (NO2 --N + NO3 --N) higher than 86%. The main mechanism of the nitrite oxidizer bacteria (NOB) inhibition was free ammonia concentrations between 3.2 and 19.5 mg NH3.l-1. The specific nitritation rates varied between 0.03 and 0.11 kg TAN. kg VSS-1.d-1, for temperatures between 15 and 34oC. Phenol showed to be suitable as carbon source for denitrifying biomass, once the volumetric application rates were lower than 0.02 kg phenol.m-3.h-1. Obeying this condition, it was possible to achieve: phenol removal efficiencies between 45 and 56%; specific phenol removal rates between 0.03 and 0.09 kg C6H5OH. kg VSS-1.d-1; specific denitritation rates between 0.03 and 0.06 kg NO2 --N . kg VSS-1.d-1 and removal efficiencies of (NO2 --N + NO3 --N) higher than 95%. During the anoxic phase, samples were collected from the reactor content for nitrophenols analyses. The results showed the presence of 2- nitrophenol (2-NP) and 4-nitrophenol (4-NP) in concentrations proportional to phenol volumetric application rate in the reactor liquid mass. The presence of those compounds in concentrations lower than 0.5 mg/L does not cause impact over the biological denitritation. The analyses accomplished in samples collected at the end of the anoxic reaction do not show the presence of 2 and 4-NP, demonstrating that these compounds can be biodegraded by a well-adapted biomass. The arrangement of the system for the treatment of coke-oven wastewater (Phase 02) over nitritation/denitritation involved the operation of two sequencing batch reactors (the main reactor and the polishing one). The operational conditions of the main reactor were manipulated to make feasible the NO2 --N accumulation at the end of the aerobic stage and promote the denitritation using the own organic matter present in the cokeoven wastewater as carbon source. As the supernatant of the main reactor presented high nitrite concentrations, this effluent was conducted to a biological denitrifying polishing reactor with ethanol as carbon source. At the end of the aerobic stage of the treatment cycles conducted in the main reactor, it was achieved: NO2 --N/ (NO2 --N + NO3 --N) higher than 88%; total nitrogen removal efficiencies higher than 60%; ammonia nitrogen removal higher than 90%. As occurred during the first phase of the investigation, the main NOB activity inhibition was the toxicity of the free ammonia concentrations (3.7 to 15.7 mg NH3.l-1) in the reactor content. At the end of anoxic stage, the NO2 --N removal efficiencies were limited by the availability of the biodegradable organic matter in the coke-oven wastewater but BOD/CODinfluent higher than 80% resulted in NO2 --N removals next to 100%. Regarding to the polishing reactor, it can be stated that the ethanol had a positive effect over the organic matter removal of the coke-oven wastewater.

Thesis (MTech(Environmental Health)--Cape Peninsula University of Technology, 2011 / Coke ovens may occur in the aluminium, steel, graphite, electrical, and construction industries. In the work area coke-oven workers may be exposed to various chemical compounds. Polycyclic aromatic hydrocarbons (PAHs), as human carcinogen, are primary compounds in coke oven emissions (COEs) generated in the coking process. Coke oven workers are often exposed to PAHs and can lead to a variety of human diseases.The primary routes of potential human exposure to coke oven emissions are inhalation and dermal contact. Occupational exposure may occur during the production of coke from coal, or while using coke to extract metals from their ores to synthesize calcium carbide, or to manufacture graphite and electrodes. Workers at coking plants and coal tar production plants, as well as the residents surrounding these plants, have a high risk of possible exposure to coke oven emissions.It is known that coke production could be carcinogenic to humans (Group-1) by IARC. There has been sufficient epidemiological evidence suggesting an etiological link between carcinogenic polycyclic aromatic hydrocarbon (PAHs) exposure and lung cancer risk among coke-oven workers. Lung cancer among coke-oven workers has been classified as one of the eight prescribed occupational cancers in China, and its incidence rate was about 10 times that of the general population. Therefore, lung cancer of coke-oven workers is still a critical issue in the field of prevention and control of occupational cancers in China.This thesis explores the various exposure levels of workers to PAHs at a steel plant in China. The measurement will focus on the exposure difference of personal sampling among workers in selected job classifications given the job descriptions and the coking process. The Benxi Steel Industry in Liaoning province of China (BXSI) was selected as the research location. Liaoning province is in the North of China and the location of various heavy industries in China. The measurements will be done two separate coke ovens in Benxi Steel Industry. One new coke oven was built in the 90's last century (coke oven N) and the other older coke oven was built in the 1940's in last century (coke oven O). In this research, the total number of employees that were selected in the sample for both coke ovens are 64 samples included 54 coke oven exposure workers and 10 non-exposure administrative workers working at the plants.

In this study, coke oven tar addition over a range of 0 – 8 wt.% was evaluated as a possible substitute for imported coals fractions. Coke oven tar used was collected from coke oven tar decanters of the by-products section of the coke making plant. Moisture content in coke oven tar varied depending on the residence time and water carryover from coke oven tar separators to storage tanks. Therefore, various moisture ranges were considered in order to observe its effect on coal blend, carbonization and coke properties. The optimum moisture content in coke oven tar was found to be 3% with a coke oven tar addition of 6 wt.% in the coal blend. At the same coke oven tar addition of 6 wt.% in the coal blend but with 6% moisture content in coke oven tar, coke properties improved, coke yield showed up to 4% decrease. On the other hand, with 1% moisture content in coke oven tar of 6 wt.% in the coal blend, coke yield increased by 1% and low coke properties such as I40 of 42.9 and Stability of 50.3 were achieved. The latter process was characterized by excessive increased in wall pressure and pushing energy. Both wall pressure and pushing energy increase are less desirable due to their detrimental effect on the physical condition of the oven walls. Furthermore, addition of coke oven tar with 1% moisture content to coal blend can be prohibited by its high viscosity. At 3% moisture content in coke oven tar addition of 6 wt.% in the coal blend, coke properties improved. When the amount of coke oven tar was increased to 8 wt.% at the optimum coke oven addition, coke yield was not affected but low CSR of 57.8 against a target of ³60 was achieved as opposed to CSR of 65.4 at 6 wt.%. Also, coke stability of 52.2 at 8 wt.% as opposed to 56.1 at 6 wt.% was achieved. Moreover, the highest I40 of 50.9 was achieved at 6 wt.% whereas with 8 wt.% coke oven tar, I40 of 47.9 was achieved. However, up to 2% decrease in coke yield was observed. Despite this 2% decrease in coke yield, coke oven tar addition is a positive and viable option based upon economic factors (i.e. this reduces the quantity and cost of imported coals and still achieves improved coke quality which result in improved blast furnace operation and better hot metal quality).

No description available.

Orientador: João Andrade de Carvalho / Resumo: Caldeiras de produção de vapor são utilizadas no setor siderúrgico para produzir e disponibilizar vapor para o processo de geração de energia e para os vários setores que necessitam de aquecimento durante a fabricação de seus produtos, como por exemplo, a vaporização de criogênicos para distribuição na planta. Portanto, caldeiras são equipamentos que necessitam ter confiabilidade. Atualmente, a CSN (siderúrgica brasileira de grande porte) possui duas caldeiras do início da década de 80 que somente partem e operam com uma chama piloto utilizando gás de coqueria, um gás que é subproduto da produção de coque em uma planta siderúrgica. Assim, para alcançar o objetivo de mais confiabilidade e flexibilidade na operação destas caldeiras, utilizou-se os métodos de índice Wobbe, corrigido pela pressão, e o método dos múltiplos índices de Weaver para avaliar a substituição do gás de coqueria pelo gás natural de modo que estas caldeiras possam operar com gás natural em caso de indisponibilidade de gás de coqueria. Mesmo que o aporte energético entre os gases seja diferente, este pode ser ajustado pela pressão do gás. A temperatura de chama adiabática não tem variação significativa, reduzindo-se apenas 1,4%. As emissões de fumaças e CO2 aumentam com a substituição, porém as emissões de NOx tem redução. A utilização do método dos múltiplos índices de Weaver para análise de intercambiabilidade demonstra que o gás natural não é um substituo para um queimador projetado para queimar gás de co... (Resumo completo, clicar acesso eletrônico abaixo) / Abstract: Steam generators are used in the steel industry to produce and supply steam process for power generation and for other sectors that need heat to manufacture their products, such as the cryogenics vaporization for distribution in the facilities. Therefore, steam generators are equipment that need to have reliability. Currently, CSN (large Brazilian steelmaker) has two steam generators from the early 1980s that only startup and operate with a pilot flame using coke oven gas, a gas that is a byproduct of coke production at a steel plant. Thus, in order to achieve the working objective, reliability and flexibility in the operation of these steam generators, the Wobbe index method, with pressure-corrected, and the Weaver's multiple index method were used to verify the coke oven replacement for natural gas, and then, these steam generators can operate with natural gas in case of coke oven gas unavailability. Results shown in the same way that the energy increase between the gases are different can be adjusted in the pressure reduction. The flame temperature has insignificant variation, only 1.4%. Off gas and CO2 emissions increase with interchangeability. However, NOx emissions are reduced. The Weaver multiple index method for interchangeability analysis demonstrates that natural gas is not a gas to replace coke oven gas in a burner designed to burn coke oven gas, but if the burner is designed to natural gas, coke oven gas may be the substitute gas. Regarding the heat input and pri... (Complete abstract click electronic access below) / Mestre

The topic of this diploma thesis is to design the co-firing of blast furnace gas and coke-oven gas. First, the stoichiometric calculation for the gas mixture was made. It is followed with the determination of basic measures of heating surfaces and with their thermal calculation. The part of the work is also the drawing documentation of the boiler.

The steel manufacturing industry is one of the largest emitters of CO2, accounting for upwards of 8.8% of all anthropogenic CO2 emissions. The governments are charging taxes on CO2 emissions, which incentivize the industry to further reduce CO2 emissions. At present, much of the CO2, produced in the steel manufacturing process occurs as a result of coke oven and blast furnace gas by-products. As such, two major strategies have been proposed to reduce steel-manufacturing-related CO2 emissions: producing more electricity via optimized combined cycle power plants (CCPP), and converting off-gas by-products into methanol (CBMeOH). The present research consists of an economic and environmental analysis of the status quo, CCPP, and CBMeOH systems for five locations: Ontario, the USA, Finland, Mexico, and China. The economic analysis considered factors such as carbon tax, electricity price, methanol price, electricity carbon intensity, power purchasing parity, and income tax. In the CCPP process, desulphurization is conducted using ProMax with MDEA as the solvent, while the CBMeOH process uses a membrane to separate the bulk H2S, with organic sulfurs such as thiophene being removed via CO2+steam reforming and middle-temperature removal. The results of the economic analysis revealed the CBMeOH plant to be the most profitable in Ontario, the USA, China, and Mexico, while the CCPP system was shown to be the most profitable in Finland. The environmental analysis was conducted using the TRACI, CML-IA, ReCiPe2016, and IMPACT2002+ tools in SimaPro V9, with the results showing the CBMeOH system to be the most environmentally option in Ontario, Finland, and China, and the CCPP system as the most environmentally friendly option in the USA and Mexico. / Dissertation / Doctor of Philosophy (PhD)

The diploma thesis deals with design of gas steam boiler with given parameters of steam. Blast furnace and coke oven gas are used as fuel. At the beginning of this work, both co-fired fuels are presented to us, their chemical analysis and stoichiometry are performed. The main part of the diploma thesis deals with the dimensioning of individual heat exchange surfaces such as steam superheaters, evaporators, economizers and air heaters. All heat exchange surfaces meet recommended parameters such as recommended steam rates, flue gas, etc. At the end, the total heat balance of the boiler is performed. Part of the work is also drawing documentation showing the main dimensions of the boiler. It is also indicated the connection of individual heat exchange surfaces.