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A simple kinetic modeling approach for aerobic stabilization of real waste activated sludge

机译:一种简单的动力学建模方法,可对真实的废活性污泥进行好氧稳定

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The objective of this study is to propose a procedure to simplify the modeling of aerobic stabilization process. In order to achieve this, the activated sludge models no. 1 (ASM1) and no. 3 (ASM3) were evaluated based on uncomplicated chemical oxygen demand and volatile suspended solid data gathered from batch aerobic digesters. The aerobic digestion period of real waste activated sludge was modeled and then the modeling results were validated at different volumetric organic loading rates. The uniqueness of given model parameters were confirmed by sensitivity analyses. According to experimental results, at the end of 30 days, the maximum volatile suspended solid removal rate was as 51.50%. The model simulations indicated the viability of both models, with regression coefficients of >0.978 without requiring the addition of any process or component to the original model structures contrary to those suggested by prior studies. According to sensitivity analyses used to determine the identifiability of estimated model parameters, the active biomass fraction, production rate of microbial products, endogenous decay rate and heterotrophic yield coefficient are the most sensitive and identifiable parameters in both models. As a result of modeling, the endogenous decay process was determined to be the main microbial mechanism involved in aerobic digestion, while the hydrolysis of particulate organic matter and removal of storage products were found as insignificant mechanisms during aerobic digestion process. Additionally, the modeling studies indicated the importance of the organic loading to achieve satisfactory organic removal since microbial kinetic rates were decreased under a threshold level of organic loading. (C) 2016 Elsevier B.V. All rights reserved.
机译:这项研究的目的是提出一种程序来简化有氧稳定过程的建模。为此,活性污泥的型号为1(ASM1),否。根据简单的化学需氧量和从分批需氧消化器中收集的挥发性悬浮固体数据评估了3(ASM3)。对真实废物活性污泥的好氧消化时间进行了建模,然后在不同体积有机负荷率下验证了建模结果。给定模型参数的唯一性通过敏感性分析得到确认。根据实验结果,在30天结束时,最大挥发性悬浮固体去除率为51.50%。模型仿真表明了这两个模型的可行性,回归系数> 0.978,而无需向原始模型结构中添加任何过程或组件,这与先前的研究相反。根据用于确定估计的模型参数可识别性的敏感性分析,活性生物质分数,微生物产品的生产率,内源衰减率和异养产量系数是这两个模型中最敏感和可识别的参数。建模的结果是,内源性腐烂过程被确定为有氧消化过程中的主要微生物机制,而有氧消化过程中颗粒有机物的水解和存储产物的去除被认为是微不足道的。另外,建模研究表明有机负荷对实现令人满意的有机去除的重要性,因为微生物动力学速率在有机负荷的阈值水平以下降低。 (C)2016 Elsevier B.V.保留所有权利。

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