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An evaluation of aerobic and anaerobic sludges as start-up material for microbial fuel cell systems

机译:评估好氧和厌氧污泥作为微生物燃料电池系统的启动材料

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The operation of microbial fuel cells (MFCs) seeded with the same quantities of aerobic or anaerobic sludge has been compared. The two sludges consisted of mixed cultures obtained from the aerobic reactor and anaerobic digester, respectively, of a municipal Wastewater Treatment Plant (WWTP). Both the sludges were diluted with their sedimentation supernatant to avoid modifying their metabolism. The results show that the type of sludge has a major impact on the performance of the system. Seeding an MFC with anaerobic acclimated sludge leads to a more rapid start-up of electricity production and the absence of a lag period. In the MFC seeded with anaerobic sludge, the steady-state operation conditions were achieved in less than 10 days, while in the aerobic sludge-seeded MFC more than 20 days were necessary to achieve this regime. The anaerobic sludge also led to better performance of the MFC. Thus, maximum power densities above 300 mW m~(-2) were obtained for such systems (i.e. two times higher than that achieved with the aerobic sludge-seeded MFC in the same setup). This better performance is a direct consequence of the greater availability of Chemical Oxygen Demand (COD) in anaerobic sludge. However, the performance is not a consequence of the coulombic efficiency in the use of the COD to produce electricity because the aerobic sludge-seeded MFC doubles this figure with respect to the anaerobic sludge-seeded system.
机译:比较了接种了相同数量的好氧或厌氧污泥的微生物燃料电池(MFCs)的运行情况。两种污泥由分别从市政废水处理厂(WWTP)的好氧反应器和厌氧消化池中获得的混合培养物组成。两种污泥均用沉淀上清液稀释,以避免改变其代谢。结果表明,污泥的类型对系统的性能有重大影响。用厌氧适应性污泥播种MFC可以更快地启动电力生产并且没有滞后时间。在接种了厌氧污泥的MFC中,可以在不到10天的时间内达到稳态操作条件,而在接种好氧污泥的MFC中,要达到这一状态则需要20天以上。厌氧污泥还导致MFC的性能更好。因此,对于这样的系统,获得了高于300 mW m〜(-2)的最大功率密度(即,在相同设置下,用好氧污泥播种的MFC所达到的功率密度高出两倍)。这种更好的性能是厌氧污泥中化学需氧量(COD)可用性更高的直接结果。但是,该性能不是使用COD发电的库仑效率的结果,因为相对于厌氧污泥播种系统,需氧污泥播种的MFC使该数字翻了一番。

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