Department of Civil and Environmental Engineering, University of Waterloo, Waterloo, Ontario, Canada.
Faculty of Science, Wilfrid Laurier University, Waterloo, Ontario, Canada.
Water Environ Res. 2019 Mar;91(3):250-258. doi: 10.1002/wer.1052. Epub 2019 Jan 28.
The impact of solids residence time (SRT) on the dynamics of phosphorus (P) removal by hydrous ferric oxide (HFO) floc was characterized through experimental and modeling studies. Three abiotic process conditions were considered in systems operated over a range of SRTs (~3 to 27 days): uptake in sequencing batch reactors (SBRs) under (a) constant and (b) dynamic P loading conditions, and (c) uptake in batch sorption tests with preformed HFO solids. P removal under all conditions was characterized by an initial period of fast removal followed by a period of slower removal until pseudo-equilibrium was reached. The initial removal rate increased with increasing P concentrations and was attributed to a larger concentration gradient between soluble- and adsorbed-phase concentrations. A kinetic model was developed and found to describe the dynamic behavior of P adsorption onto HFO floc under all conditions tested. A consistent mass transfer rate coefficient (k) was found to describe mass transfer over a range of SRTs for low initial P concentrations. At elevated SRTs (23-27 days) and elevated influent P concentrations, k values were found to deviate from those estimated at reduced SRTs. Differences in process mixing conditions were reflected in the estimated rate coefficients (k). Integration of the kinetic model with existing equilibrium models in wastewater process simulators will improve the ability to predict P uptake onto HFO floc under dynamic loading conditions in water resource recovery facilities. Models that consider the kinetics of P uptake will be particularly relevant for facilities that are required to achieve ultralow P concentrations. PRACTITIONER POINTS: This work provides a kinetic model that can be integrated with existing equilibrium models in wastewater process simulators to improve the ability to predict P uptake onto HFO floc under dynamic loading conditions. This research can be used to assist WRRFs to achieve ultralow effluent P requirements.
通过实验和建模研究,考察了固体停留时间(SRT)对水合氧化铁(HFO)絮体去除磷(P)动力学的影响。在 SRT(~3 至 27 天)范围内运行的系统中,考虑了三种非生物过程条件:(a)在恒磷负荷和(b)动态磷负荷条件下序批式反应器(SBR)中的吸收,以及(c)使用预先形成的 HFO 固体进行批量吸附试验中的吸收。所有条件下的 P 去除均表现为快速去除初期,随后为缓慢去除期,直至达到假平衡。初始去除速率随 P 浓度的增加而增加,这归因于可溶相与吸附相间浓度的较大浓度梯度。开发了一个动力学模型,发现该模型可描述在所有测试条件下 HFO 絮体上 P 吸附的动态行为。发现一致的传质速率系数(k)可描述在低初始 P 浓度范围内的传质过程。在较高的 SRT(23-27 天)和较高的进水 P 浓度下,发现 k 值偏离了在较低 SRT 下估计的值。过程混合条件的差异反映在估计的速率系数(k)中。将动力学模型与废水处理模拟器中的现有平衡模型集成,将提高在水资源回收设施中动态负荷条件下预测 HFO 絮体对 P 的吸收能力。考虑 P 吸收动力学的模型对于需要实现超低 P 浓度的设施将特别相关。实践者要点:这项工作提供了一个动力学模型,可以与废水处理模拟器中的现有平衡模型集成,以提高在动态负荷条件下预测 HFO 絮体对 P 的吸收能力。这项研究可用于帮助 WRRF 实现超低出水 P 要求。