Department of Civil Engineering and Applied Mechanics, McGill University, 817 Sherbrooke St. West, Montreal, Quebec H3A 0C3, Canada.
Water Res. 2012 Sep 1;46(13):3999-4008. doi: 10.1016/j.watres.2012.05.009. Epub 2012 May 16.
Electro-dewatering is an energy-efficient technology in which an electric field can increase the dryness of biosolids from secondary wastewater treatment from 15% w/w to 30-50% w/w. Here, we address bacterial pathogen indicators inactivation (total coliforms, Escherichia coli and aerobic endospores) during electro-dewatering, investigating the roles of electrochemically generated oxidants, extreme pH, and high temperature (from Joule heating). Our results demonstrate that temperature is the primary factor affecting total coliforms and E. coli inactivation. First, several electro-dewatering cycles were used to increase sludge temperature to about 100 °C after 6 min, during which time the average pH decreased from 7 to 3.6 after 10 min. Total coliforms and E. coli MPNs reached their detection limits after 6 min (with 4-5 logs of inactivation for total coliforms and 3-4 logs for E. coli). In contrast, aerobic endospores were not inactivated under these conditions; rather, their germination appeared to be stimulated by 6-8 min of electro-dewatering. Second, the dewatering cake was separated into four horizontal layers. After 8 min of electro-dewatering, the pH in the top layers decreased to 3, whereas the pH in the bottom layers increased to 8. Inactivation of total coliforms and E. coli in the sludge cake was similar in all layers, increasing with time, suggesting that oxidants and extreme pH are secondary inactivation factors. Finally, electrodes were cooled to maintain a temperature less than 34 °C. Although pH decreased significantly after 12 min of electro-dewatering, there was no significant bacterial pathogen indicator inactivation at low temperature.
电脱水是一种节能技术,它可以使二级废水处理中的生物固体的干燥度从 15%w/w 增加到 30-50%w/w。在这里,我们研究了电脱水过程中细菌病原体指标(总大肠菌群、大肠杆菌和需氧芽孢)的灭活情况,考察了电化学产生的氧化剂、极端 pH 值和高温(焦耳加热)的作用。我们的结果表明,温度是影响总大肠菌群和大肠杆菌灭活的主要因素。首先,经过几个电脱水循环,在 6 分钟后将污泥温度提高到 100°C 左右,在此期间,平均 pH 值在 10 分钟内从 7 下降到 3.6。总大肠菌群和大肠杆菌 MPN 在 6 分钟后达到检测极限(总大肠菌群有 4-5 个对数的灭活,大肠杆菌有 3-4 个对数的灭活)。相比之下,在这些条件下,需氧芽孢并没有被灭活;相反,它们的萌发似乎受到 6-8 分钟的电脱水的刺激。其次,将脱水饼分成四个水平层。经过 8 分钟的电脱水后,顶层的 pH 值下降到 3,而底层的 pH 值上升到 8。污泥饼中总大肠菌群和大肠杆菌的灭活在所有层中相似,随着时间的增加而增加,表明氧化剂和极端 pH 值是次要的灭活因素。最后,电极被冷却以保持温度低于 34°C。尽管电脱水 12 分钟后 pH 值显著下降,但在低温下没有显著的细菌病原体指标灭活。