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A modified anaerobic digestion process with chemical sludge pre-treatment and its modelling

机译:化学污泥预处理的改进厌氧消化工艺及其建模

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Activated Sludge Models (ASMs) assume an unbiodegradable organic particulate fraction in the activated sludge, which is derived from the decay of active microorganisms in the sludge and/or introduced from wastewater. In this study, a seasonal change of such activated sludge constituents in a municipal wastewater treatment plant was monitored for 1.5 years. The chemical oxygen demand ratio of the unbiodegradable particulates to the sludge showed a sinusoidal pattern ranging from 40 to 65% along with the change of water temperature in the plant that affected the decay rate. The biogas production in a laboratory-scale anaerobic digestion (AD) process was also affected by the unbiodegradable fraction in the activated sludge fed. Based on the results a chemical pretreatment using H_2O_2 was conducted on the digestate to convert the unbiodegradable fraction to a biodegradable one. Once the pre-treated digestate was returned to the digester, the methane conversion increased up to 80% which was about 2.4 times as much as that of the conventional AD process, whilst 96% of volatile solids in the activated sludge was digested. From the experiment, the additional route of the organic conversion processes for the inert fraction at the pre-treatment stage was modelled on the ASM platform with reasonable simulation accuracy.
机译:活性污泥模型(ASM)假设活性污泥中存在不可生物降解的有机颗粒部分,这是由污泥中活性微生物的腐烂和/或从废水中引入的。在这项研究中,监测了市政污水处理厂中此类活性污泥成分的季节性变化,持续了1.5年。不可生物降解的颗粒与污泥的化学需氧量比例呈正弦曲线,变化范围为40%至65%,并且工厂中的水温变化影响了腐烂率。实验室规模厌氧消化(AD)过程中的沼气生产也受到进料的活性污泥中不可生物降解部分的影响。基于该结果,在消化液上进行了使用H_2O_2的化学预处理,将不可生物降解的馏分转化为可生物降解的馏分。一旦将预处理的消化物返回到消化器中,甲烷转化率将提高至80%,约为传统AD工艺的2.4倍,而活性污泥中96%的挥发性固体被消化了。从实验中,在ASM平台上以合理的模拟精度对惰性阶段有机物转化过程在惰性阶段的附加路线进行了建模。

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