“…26 Unfortunately, these conditions are not found in actual HTL-AP product effluents, which contain significant concentrations of foreign ions and polar organic compounds, 7,25,27 higher ionic strength (0.2−0.4 M), 25,28 and nonequimolar Mg/NH 3 −N/P ratios. 29−32 Few studies have investigated the struvite crystallization thermodynamics and kinetics in real wastewaters, adopting different kinetic models, e.g., linear growth rate, 33 first-order kinetics, 26 population balance, 34 and size-dependent growth 35 models. To design a fluidized bed reactor for struvite production, a recent study 36 proposed three solid−liquid flow models, i.e., complete mixing of liquid and bed, plug flow of liquid and perfect classification of the bed, and plug flow of liquid and complete mixing of the bed, incorporated with reduced thermodynamic and growth kinetic models; the aim of the study was to improve previously proposed flow models by Rahaman et al 37 and Burns et al 38 However, those studies assume an ideal condition, neglecting the change of chemical thermodynamic properties at different temperatures and pH, e.g., ionic strength and effective concentration or activity of the reacting ions, during crystallization and the possibility of side reactions caused by foreign ions, e.g., hydroxyapatite formation due to Ca 2+ presence.…”