Department of Green Chemistry and Technology, Coupure Links 653, 9000, Gent, Ghent University, Belgium.
Department of Biotechnology, Delft University of Technology, Van der Maasweg 9, 2629 HZ, Delft, the Netherlands.
Water Res. 2020 Jul 1;178:115844. doi: 10.1016/j.watres.2020.115844. Epub 2020 Apr 21.
Gas bubbles are introduced in water to absorb or strip volatile substances in a variety of unit operations, for example during (waste)water treatment. To calculate the transfer rate of substances between the liquid phase and the gas phase, different assumptions have been made in literature regarding the gas phase composition and hydraulic pressure, which both vary along the reactor height. In this study, analytical expressions were derived for the total (macroscopic) liquid-gas transfer rate, using either the complete gradients of the mole fraction and pressure (comprehensive approach) or a uniform value, for one or both of them. Simulations with the comprehensive model were performed to understand the effect of the type of volatile substance and of the reactor design and operating conditions on the total liquid-gas transfer rate. These effects were found to be highly interactive and often non-linear. Next, the simulation results of the comprehensive model were compared with those from models that assume either a uniform mole fraction or a uniform pressure in the complete reactor volume. This illustrated that for soluble substances, the mole fraction gradient strongly affects the total liquid-gas transfer rate, while the pressure gradient became only important under operating conditions that promote stripping (i.e., for a high concentration in the liquid phase and low concentration in the inlet gas). For very poorly soluble substances, the pressure became more important under conditions that promote absorption. These results on the importance of the mole fraction and pressure gradients remained equally valid when explicitly considering a typical variation of the volumetric overall transfer coefficient (Ka) along the reactor height. Finally, a simple and fast procedure was made available through a spreadsheet to select appropriate simplifying assumptions in reactor or plant-wide models. By applying the procedure to oxygen (O), carbon dioxide (CO), methane (CH), nitrous oxide (NO) and nitrogen gas (N) in an aerobic biological wastewater treatment reactor, it was demonstrated that some common simplifications can lead to significant errors, for which corrections were proposed.
气体气泡被引入水中以吸收或去除各种单元操作中的挥发性物质,例如在(废水)处理过程中。为了计算液相和气相之间物质的传递速率,文献中对气相组成和液压有不同的假设,它们沿着反应器高度变化。在这项研究中,使用完整的摩尔分数和压力梯度(综合方法)或它们中的一个或两个的均匀值,推导出了总(宏观)气-液传递速率的分析表达式。使用综合模型进行模拟,以了解挥发性物质的类型以及反应器设计和操作条件对总气-液传递速率的影响。发现这些影响高度交互且通常是非线性的。然后,将综合模型的模拟结果与假设整个反应器体积中的摩尔分数或压力均匀的模型的模拟结果进行比较。这表明,对于可溶性物质,摩尔分数梯度强烈影响总气-液传递速率,而压力梯度仅在促进汽提的操作条件下(即液相中浓度高而入口气体中浓度低)才变得重要。对于非常难溶的物质,在促进吸收的条件下压力变得更为重要。当明确考虑沿反应器高度的体积总传质系数(Ka)的典型变化时,这些关于摩尔分数和压力梯度重要性的结果仍然有效。最后,通过电子表格提供了一种简单快速的程序,以便在反应器或工厂范围内的模型中选择适当的简化假设。通过将该程序应用于好氧生物废水处理反应器中的氧气(O)、二氧化碳(CO)、甲烷(CH)、氧化亚氮(NO)和氮气(N),证明了一些常见的简化可能会导致显著的错误,并提出了纠正措施。