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Leaching and Crystallization Methods for Chloride and Potassium Removal from Recovery Boiler Fly Ash

机译:氯化物浸出和结晶方法,回收锅炉粉煤灰去除

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Chloride and potassium are harmful non-process elements in the kraft chemical recovery cycle. In high concentrations they can cause severe corrosion and fouling of the recovery boiler heat exchangers. Traditionally their levels in circulation have been controlled by dumping a portion of ESP ash. However, environmental concerns and cost of make-up chemicals are increasing the interest towards more affordable and environmentally friendly removal methods. This paper presents the principles of two common chloride and potassium removal methods: ash leaching and evaporative recrystallization. Experiences and the suitability of these two methods in different situations are reviewed based on operational data collected from recent installations. In the ash leaching process chloride and potassium are leached out of ESP ash with hot water. In ash crystallization the ash is completely dissolved in water and the mixture is evaporated until sodium sulfate crystallizes from the solution. In both processes valuable sodium is returned to the recovery cycle by mixing the solids with heavy black liquor while chloride and potassium are removed by purging the liquid reject. When comparing the two processes, leaching is simple and the more straightforward option while crystallization requires a bit more sophisticated process design. The composition of ESP ash has a major impact on process performance but generally the crystallization method yields better removal and recovery efficiencies. Selecting the most suitable removal method for a mill is always case specific since it depends on raw materials, make-up chemicals and degree of closure of the mills' chemical cycles. As a rule of thumb, leaching is most suitable for smaller removal needs and retrofits while crystallization can handle larger capacities, making it a good option for new and larger mill projects.
机译:氯化物和钾是牛皮纸化学回收循环中有害的非工艺元素。在高浓度下,它们会导致回收锅炉热交换器的严重腐蚀和污垢。传统上,通过倾倒一部分ESP灰来控制它们在循环中的水平。然而,环境问题和化妆化学品的成本正在增加对更实惠和环保的去除方法的利益。本文介绍了两种常见的氯化物和钾去除方法的原理:灰浸出和蒸发再结晶。基于从最近安装中收集的操作数据审查了这两种方法在不同情况下的经验和适用性。在灰烬浸出过程中,氯化物和钾用热水浸出ESP灰分。在灰分结晶中,灰分完全溶解在水中,蒸发混合物直至硫酸钠从溶液中结晶。在这两种方法中,通过将固体与重黑液混合,当氯化物和钾通过吹扫液体拒绝除去氯化物和钾来返回回收循环。在比较这两个过程时,浸出是简单的,并且结晶需要更复杂的过程设计的同时更简单且更直接的选择。 ESP灰的组成对工艺性能的重大影响,但通常结晶方法产生更好的去除和恢复效率。选择最合适的轧机的去除方法总是具体的,因为它取决于原材料,化妆品和磨机的闭合程度。通常,浸出最适合较小的去除需求和改造,同时结晶可以处理更大的容量,使其成为新的和较大轧机项目的良好选择。

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