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在同时和顺序交替投加污染物条件下2-氟苯甲酸酯和二氯甲烷的生物降解

Biodegradation of 2-fluorobenzoate and dichloromethane under simultaneous and sequential alternating pollutant feeding.

作者信息

Osuna M Begoña, Sipma Jan, Emanuelsson Maria A E, Carvalho M Fátima, Castro Paula M L

机构信息

Escola Superior de Biotecnologia, Universidade Católica Portuguesa, 4200-072 Porto, Portugal; CSIC-CEAB, Blanes, Spain.

出版信息

Water Res. 2008 Aug;42(14):3857-69. doi: 10.1016/j.watres.2008.05.011. Epub 2008 Jun 21.

Abstract

Two up-flow fixed-bed reactors (UFBRs), inoculated with activated sludge and operated for 162 days, were fed 1mmolL(-1)d(-1) with two model halogenated compounds, 2-fluorobenzoate (2-FB) and dichloromethane (DCM). Expanded clay (EC) and granular activated carbon (GAC) were used as biofilm carrier. EC did not have any adsorption capacity for both model compounds tested, whereas GAC could adsorb 1.3mmolg(-1) GAC for 2-FB and 4.5mmolg(-1) GAC for DCM. Both pollutants were degraded in both reactors under simultaneous feeding. However, biodegradation in the EC reactor was more pronounced, and re-inoculation of the GAC reactor was required to initiate 2-FB degradation. Imposing sequential alternating pollutant (SAP) feeding caused starvation periods in the EC reactor, requiring time-consuming recovery of 2-FB biodegradation after resuming its feeding, whereas DCM degradation recovered significantly faster. The SAP feeding did not affect performance in the GAC reactor as biodegradation of both pollutants was continuously observed during SAP feeding, indicating the absence of true starvation.

摘要

两个上流式固定床反应器(UFBR)接种活性污泥并运行162天,以1mmolL(-1)d(-1)的剂量投加两种模型卤代化合物,即2-氟苯甲酸盐(2-FB)和二氯甲烷(DCM)。膨胀黏土(EC)和颗粒活性炭(GAC)用作生物膜载体。EC对所测试的两种模型化合物均无吸附能力,而GAC对2-FB的吸附量为1.3mmolg(-1) GAC,对DCM的吸附量为4.5mmolg(-1) GAC。在同时投加的情况下,两种污染物在两个反应器中均被降解。然而,EC反应器中的生物降解更为明显,需要对GAC反应器重新接种以启动2-FB的降解。采用顺序交替投加污染物(SAP)导致EC反应器出现饥饿期,恢复投加2-FB后其生物降解需要耗时恢复,而DCM降解的恢复速度明显更快。SAP投加对GAC反应器的性能没有影响,因为在SAP投加期间持续观察到两种污染物的生物降解,表明不存在真正的饥饿状态。

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