Hamdaoui Oualid, Alghyamah Abdulaziz
Chemical Engineering Department, College of Engineering, King Saud University, P.O. Box 800, 11421 Riyadh, Saudi Arabia.
Chemical Engineering Department, College of Engineering, King Saud University, P.O. Box 800, 11421 Riyadh, Saudi Arabia.
Ultrason Sonochem. 2023 Nov;100:106606. doi: 10.1016/j.ultsonch.2023.106606. Epub 2023 Sep 21.
The pseudo-first and pseudo-second order equations have been the most commonly used models to characterize the sonolytic disappearance kinetics of nonvolatile pollutants in aqueous media. In this work, the general rate law model, i.e., pseudo-nth order kinetics equation, was applied for the first time to the sono-decomposition of different nonvolatile organic pollutants, naphthol blue black (NBB), furosemide (FSM), 4-isopropylphenol (4-IPP), and rhodamine B (RhB), in water. It was shown that the general rate law for a chemical reaction would apply to the kinetics of sonochemical decomposition. It is not feasible to set the order of ultrasonic pollutant degradation kinetics to pseudo-first or pseudo-second, as is typically used in numerous studies. The sonochemical oxidation reaction has a fractional order, the order is often non-integer, which frequently indicates a complex sonolytic decomposition reaction mechanism. The degradation mechanism of NBB and RhB does not change with the initial substrate concentration. They are ultrasonically degraded by hydroxyl radicals both in the bulk liquid solution and at the liquid/bubble interfacial layer. The destruction mechanism of FSM and 4-IPP changes as the initial contaminant concentration changes. At low initial substrate concentrations, these pollutants are oxidized mainly by reaction with hydroxyl radicals in the bulk liquid solution and at the interfacial shell of the cavitation bubbles. At high initial substrate concentrations, FSM and 4-IPP are degraded by thermal destruction in the liquid/bubble interfacial layer and by OH radicals both in the bulk liquid solution and at the liquid/bubble interfacial layer. Additionally, the pseudo-nth order model predicts very well the sonolytic degradation at various sonication frequencies and intensities. The general rate law expression should be used to assess the real kinetics order of the sonolytic destruction process without any predetermined assumptions or constraints.
拟一级和拟二级方程是表征水相中难挥发污染物声解消失动力学最常用的模型。在本工作中,通用速率定律模型,即拟n级动力学方程,首次应用于水中不同难挥发有机污染物萘酚蓝黑(NBB)、速尿(FSM)、4-异丙基苯酚(4-IPP)和罗丹明B(RhB)的声分解。结果表明,化学反应的通用速率定律适用于声化学分解动力学。将超声污染物降解动力学的级数设定为拟一级或拟二级是不可行的,而这在众多研究中通常是这样做的。声化学氧化反应具有分数级,该级数通常为非整数,这常常表明存在复杂的声解分解反应机理。NBB和RhB的降解机理不随初始底物浓度而变化。它们在本体液体溶液和液/泡界面层均通过羟基自由基进行超声降解。FSM和4-IPP的破坏机理随初始污染物浓度的变化而改变。在低初始底物浓度下,这些污染物主要通过与本体液体溶液和空化泡界面壳层中的羟基自由基反应而被氧化。在高初始底物浓度下,FSM和4-IPP在液/泡界面层通过热破坏以及在本体液体溶液和液/泡界面层均通过羟基自由基进行降解。此外,拟n级模型能很好地预测不同超声频率和强度下的声解降解。应使用通用速率定律表达式来评估声解破坏过程的实际动力学级数,而无需任何预先设定的假设或限制。