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首页> 外文期刊>Developments in chemical engineering and mineral processing >The Deposition of Calcium Oxalate and Amorphous Silica Scale under Dynamic Conditions which Simulate Sugar Mill Evaporators
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The Deposition of Calcium Oxalate and Amorphous Silica Scale under Dynamic Conditions which Simulate Sugar Mill Evaporators

机译:模拟糖厂蒸发器的动态条件下草酸钙和非晶硅垢的沉积

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Composite fouling of calcium oxalate monohydrate (COM) and amorphous silica (SiO_2) in sugar mill evaporators poses a major processing problem. The significance of COM-SiO_2 interactions during composite scale formation has been recognized previously and their effects on the fouling behaviour of both species have been demonstrated in batch tests. This work investigates the mechanisms of composite fouling of COM and SiO_2 in a dynamic system under subcooled flow-boiling and continuous evaporation. The experimental approach used in this study is novel. It simulates the operation cycle in the latter effects of sugar mill evaporators within one experimental run whilst maintaining a relatively simple process. The composite fouling behaviour of COM and SiO_2 has been tested in aqueous solutions with a range of COM/SiO_2 supersaturation ratios to determine the critical feed composition at which the maximum degree of composite fouling occurred. The synergistic effect of COM on composite fouling occurred at an intermediate concentration of COM (50 ppm) whereas antagonism was obtained at either low or high COM concentration (20 and 100 ppm). This may be due to changes in the magnitude of the interfacial energy barrier between the surface of the particles and the wall, and to the differences in the physical properties of the foulins species such as varticle size.
机译:草糖蒸发器中草酸钙一水合物(COM)和无定形二氧化硅(SiO_2)的复合结垢是一个主要的加工问题。先前已经认识到复合垢形成过程中COM-SiO_2相互作用的重要性,并已通过分批测试证明了它们对两种污垢行为的影响。本文研究了过冷沸腾和连续蒸发条件下动态系统中COM和SiO_2复合结垢的机理。在这项研究中使用的实验方法是新颖的。它在一个实验运行中模拟糖厂蒸发器的后一种作用的运行周期,同时保持相对简单的过程。已经在一定范围的COM / SiO_2过饱和比的水溶液中测试了COM和SiO_2的复合污垢行为,以确定在最大程度发生复合污垢时的关键进料组成。在中等浓度的COM(50 ppm)下,COM对复合污垢产生了协同作用,而在低或高的COM浓度(20和100 ppm)下均产生了拮抗作用。这可能是由于颗粒表面和壁之间的界面能垒的大小变化,以及叶藻种类的物理特性(例如,囊泡大小)的差异。

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