共查询到18条相似文献,搜索用时 531 毫秒
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建立了以煤为辅助燃料,有机废液在流化床中焚烧密相区及稀相区的热平衡方程,在此基础上计算获得废液在密相区的焚烧量占总处理量的份额,密相区焚烧温度,炉膛膛出口温度的影响关系曲线。计算结果表明:废液在密相区焚烧量占总焚烧量的70%时,可使密相区温度与炉膛出口温度基本一致的;密相区温度宜控制在850℃~900℃,可节省辅助燃料;炉膛出口空气过剩系数宜控制在1.7以内,同时尽可能提高预热空气温度。此结果为流化床焚烧炉的设计与运行提供理论依据。 相似文献
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以德国Hauptklarwerk Stuttgart-Muhlhausen污水处理厂的两座鼓泡式流化床焚烧炉为主要研究对象,针对该厂的污泥焚烧区,从离心脱水、干燥、焚烧、烟气洗涤装置等一系列处理单元的工作原理、工艺流程、热量平衡计算的分析,来全面认识流化床焚烧工艺的最佳焚烧工况及运行参数(炉温、过量空气比等). 相似文献
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介绍焚烧工艺的发展历史和现状,重点介绍污泥焚烧工艺中流化床焚烧炉的结构和特点,以及影响污泥焚烧的因素,分析污泥焚烧工艺的发展趋势。 相似文献
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污水处理厂下水污泥一般含水率为80%,其余的20%中含有各种有害物质,焚烧是最彻底的无害化处理方法。鼓泡流化床焚烧炉成为主要的污泥焚烧装置。不添加煤等辅助燃料才能保证焚烧处理的环保性使烟气中的污染物不被稀释。烘干后含水率达到~62%,应用基低位热值达到650kcal/kg以上的污泥才能达到焚烧条件。焚烧系统由污泥进料系统、鼓泡流化床焚烧炉、送风系统、排渣及砂循环系统四个单元构成。污泥进料系统中料斗的形状应能防止斗内污泥搭桥、堵塞。鼓泡流化床焚烧炉应保证q3、q4损失接近于0。送风系统中一、二次风机抽气口设置在污泥池内来避免臭气外泄。并设置高温空气预热器使热风温度最高达到500℃。排渣及砂循环系统应保证炉膛密封。 相似文献
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以某热电厂450t/h循环流化床锅炉运行实测数据为基础,在锅炉密相区和稀相区分别建立热平衡方程式,计算循环流化床锅炉密相区、稀相区内的传热系数,并提出了稀相区内以对流为主的对流-辐射模型,新的计算方法可直接计算循环流化床锅炉稀相区辐射传热在总的传热中占的比率。图5参7 相似文献
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循环床锅炉沿床高的烟气浓度及燃烧份额分布测试结果证明,鼓泡流化床和循环流化床的重要差异表现为密相区燃烧行为的根本不同,由于床料平均粒径较低,循环床密相区的流动不同于鼓泡床,导致气固两相之间的传质阻力增加,从而影响燃烧反应,密相区的燃烧行为表现为欠氧。循环床锅炉沿床高乃至分离器都有燃烧反应发生,建立了考虑气固相间传质阻力的流化床密相区燃烧模型,并与实际循环流化床锅炉的测试数据比较,计算结果与测试值比较吻合。 相似文献
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循环流化床中颗粒内循环与循环流化床锅炉的设计 总被引:2,自引:0,他引:2
本文从循环床锅炉密相区的热平衡计算出发,探讨了密相区内受热面面积及密相区高度与飞灰循环倍率、密相区燃烧份额的关系,并以4种典型煤种为例,分析了煤种变化对密相区高度的影响。设计计算和运行经验相结合,在密相区热平衡分析中,引入了床内粒子循环的概念,从而对密相区内热平衡和受热面面积的确定有更深入的理解。 相似文献
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流化床内气固两相流动一直是实验研究和数值模拟的热点。基于Eulerian双流体模型,本文建立了流化床内的气固两相流动模型,采用FLUENT软件对流化床密相区两相流动特性、床内气泡的产生运动和爆裂等特性进行了数值模拟。模型中,将颗粒相看作是连续介质,建立与气相相同形式的数学模型;采用了离散介质动力理论,引入颗粒温度来描述固相粘性应力,并用气固曳力进行气固两相耦合。模拟得到了气泡产生、运动和爆裂的变化过程,与实验结果相一致。采用不同的曳力模型对流化床稠密两相流动进行了模拟,与Kuipers实验对比,结果表明采用Gidaspow曳力模型描述流化床稠密两相流动特性更准确。 相似文献
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《Energy Conversion and Management》2005,46(7-8):1165-1178
Fluidized bed combustion technology has been widely used as the new, flexible, multi-fuel boiler for waste combustion and energy recovery from low grade fuels. However, problems such as low thermal efficiency, high emissions, bed agglomeration etc. are still encountered in the operation of fluidized beds. Valuable experiences were gained from two case studies recently conducted regarding wastes combustion in industrial scale fluidized beds.In the first case, the performance of a fluidized bed combustor for energy recovery from oil sludge was evaluated during the commissioning trials. Apart from the sludge characterization and bed material analysis, the combustion efficiency, solid flow balance and on stack emission of CO, SOx and NOx were investigated, as well as the fluidization quality. Although the system was operated with good combustion efficiency (>99.9%), sulfur dioxide emission (>1000 ppm) was found to be substantially higher than the allowable discharge limit. It was recommended to increase the limestone feed rate in order to meet the SO2 emission standard, and subsequently, installation of a cyclone is suggested to remove the potentially significant increase in ash and fine particles.The second case study focused on the bed agglomeration observed in a fluidized bed incinerator where a burning blend of three wastes (i.e. carbon soot, biosludge and fuel oil) is involved. To understand the mechanisms and related chemistry, several analytical approaches are employed to identify the bed materials (fresh sand and degrader sand) and the clinkers formed from full scale incinerator tests. The formation of clinker is believed to follow the mechanism of partial melting and/or reactive liquid sintering. The effects of temperature and blending ratio are tested in a muffle furnace. Carbon soot is believed to be more susceptible than the other two fuels. Thermodynamic multi-phase multi-component equilibrium (TPCE) calculations predict that the main low melting point species are predominant under the oxidizing condition, suggesting that reducing conditions might be favorable to restrain bed agglomeration. This study provides valuable information for better understanding of the chemistry related to clinker formation; it also helps in developing methods for control and possible elimination of the bed agglomeration problem for the design fuels. 相似文献