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首页> 外文期刊>Water, Air, and Soil Pollution >Biofiltration of Chloroform in a Trickle Bed Air Biofilter Under Acidic Conditions
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Biofiltration of Chloroform in a Trickle Bed Air Biofilter Under Acidic Conditions

机译:酸性条件下滴流床空气生物滤池中氯仿的生物滤池

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摘要

In this paper, the application of biofiltration is investigated for controlled removal of gas phase chloroform through cometabolic degradation with ethanol. A trickle bed air biofilter (TBAB) operated under acidic pH 4 is subjected to aerobic biodegradation of chloroform and ethanol. The TBAB is composed of pelleted diatomaceous earth filter media inoculated with filamentous fungi species, which served as the principle biodegrading microorganism. The removal efficiencies of 5 ppm(v) of chloroform mixed with different ratios of ethanol as cometabolite (25, 50, 100, 150, and 200 ppm(v)) ranged between 69.9 and 80.9%. The removal efficiency, reaction rate kinetics, and the elimination capacity increased proportionately with an increase in the cometabolite concentration. The carbon recovery from the TBAB amounted to 69.6% of the total carbon input. It is postulated that the remaining carbon contributed to excess biomass yield within the system. Biomass control strategies such as starvation and stagnation were employed at different phases of the experiment. The chloroform removal kinetics provided a maximum reaction rate constant of 0.0018 s(-1). The highest ratio of chemical oxygen demand (COD)(removal)itrogenutilization was observed at 14.5. This study provides significant evidence that the biodegradation of a highly chlorinated methane can be favored by cometabolism in a fungi-based TBAB.
机译:在本文中,研究了生物过滤在通过乙醇的代谢分解可控地去除气相氯仿中的应用。对在酸性pH 4下运行的滴流床空气生物滤池(TBAB)进行氯仿和乙醇的需氧生物降解。 TBAB由接种有丝状真菌物种的硅藻土颗粒过滤介质组成,可作为主要的生物降解微生物。 5 ppm(v)的氯仿与不同比例的乙醇作为代谢物(25、50、100、150和200 ppm(v))混合时的去除效率介于69.9%和80.9%之间。去除效率,反应速率动力学和消除能力随合成代谢物浓度的增加而成比例增加。 TBAB的碳回收量占总碳输入量的69.6%。据推测,剩余的碳导致系统内过量的生物质产量。在实验的不同阶段采用了生物量控制策略,例如饥饿和停滞。氯仿去除动力学提供最大反应速率常数为0.0018 s(-1)。观察到最高的化学需氧量(COD)/去除氮利用率为14.5。这项研究提供了重要的证据,证明基于真菌的TBAB中的新陈代谢可以促进高度氯化甲烷的生物降解。

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