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Modeling of organic substrate transformation in the high-rate activated sludge process

机译:高速活性污泥工艺中有机基质转化的建模

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This study describes the development of a modified activated sludge model No. 1 framework to describe the organic substrate transformation in the high-rate activated sludge (HRAS) process. New process mechanisms for dual soluble substrate utilization, production of extracellular polymeric substances (EPS), absorption of soluble substrate (storage), and adsorption of colloidal substrate were included in the modified model. Data from two HRAS pilot plants were investigated to calibrate and to validate the proposed model for HRAS systems. A subdivision of readily biodegradable soluble substrate into a slow and fast fraction were included to allow accurate description of effluent soluble chemical oxygen demand (COD) in HRAS versus longer solids retention time (SRT) systems. The modified model incorporates production of EPS and storage polymers as part of the aerobic growth transformation process on the soluble substrate and transformation processes for flocculation of colloidal COD to particulate COD. The adsorbed organics are then converted through hydrolysis to the slowly biodegradable soluble fraction. Two soluble substrate models were evaluated during this study, i.e., the dual substrate and the diauxic models. Both models used two state variables for biodegradable soluble substrate (S-Bf and S-Bs) and a single biomass population. The A-stage pilot typically removed 63% of the soluble substrate (S-B) at an SRT <0.13 d and 79% at SRT of 0.23 d. In comparison, the dual substrate model predicted 58% removal at the lower SRT and 78% at the higher SRT, with the diauxic model predicting 32% and 70% removals, respectively. Overall, the dual substrate model provided better results than the diauxic model and therefore it was adopted during this study. The dual substrate model successfully described the higher effluent soluble COD observed in the HRAS systems due to the partial removal of S-Bs, which is almost completely removed in higher SRT systems.
机译:这项研究描述了改良的1号活性污泥模型框架的发展,以描述高速率活性污泥(HRAS)过程中有机基质的转化。修改后的模型中包括了双重可溶性底物利用,细胞外聚合物(EPS)的产生,可溶性底物的吸收(储存)和胶体底物吸附的新工艺机制。研究了来自两个HRAS中试工厂的数据,以校准和验证HRAS系统的建议模型。将易生物降解的可溶性底物细分为慢速组分和快速馏分,以准确描述HRAS中的可溶性可溶性化学需氧量(COD)与较长的固体保留时间(SRT)系统。修改后的模型将EPS和存储聚合物的生产作为可溶基质上需氧生长转化过程的一部分,以及将胶体COD絮凝成颗粒COD的转化过程的一部分。然后,吸附的有机物通过水解转化为生物可缓慢降解的可溶性部分。在本研究中评估了两种可溶性底物模型,即双重底物模型和双分子模型。两种模型都使用了两个状态变量来表示可生物降解的可溶性底物(S-Bf和S-Bs)和单个生物量。在SRT <0.13 d时,A级中试通常去除63%的可溶性底物(S-B),在SRT为0.23 d时去除79%。相比之下,双底物模型预测较低的SRT去除58%,而较高的SRT去除78%,双生模型预测分别去除32%和70%。总体而言,双底物模型提供的结果优于双星模型,因此在本研究中被采用。双底物模型成功地描述了由于部分去除S-B而在HRAS系统中观察到的更高的废水可溶性COD,而在更高的SRT系统中几乎完全去除了S-B。

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