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生物滤池和生物滴滤池对苯乙烯废气排放的削减:填料和接种程序的比较

Abatement of styrene waste gas emission by biofilter and biotrickling filter: comparison of packing materials and inoculation procedures.

作者信息

Pérez M C, Álvarez-Hornos F J, Portune K, Gabaldón C

机构信息

Research Group GI2AM, Department of Chemical Engineering, Universitat de València, Av. de la Universitat s/n, 46100, Burjassot, Spain.

出版信息

Appl Microbiol Biotechnol. 2015 Jan;99(1):19-32. doi: 10.1007/s00253-014-5773-9. Epub 2014 May 6.

Abstract

The removal of styrene was studied using two biofilters packed with peat and coconut fibre (BF1-P and BF2-C, respectively) and one biotrickling filter (BTF) packed with plastic rings. Two inoculation procedures were applied: an enriched culture with strain Pseudomonas putida CECT 324 for BFs and activated sludge from a municipal wastewater treatment plant for the BTF. Inlet loads (ILs) between 10 and 45 g m(-3) h(-1) and empty bed residence times (EBRTs) from 30 to 120 s were applied. At inlet concentrations ranging between 200 and 400 mg Nm(-3), removal efficiencies between 70 % and 95 % were obtained in the three bioreactors. Maximum elimination capacities (ECs) of 81 and 39 g m(-3) h(-1) were obtained for the BF1-P and BF2-C, respectively (IL of 173 g m(-3) h(-1) and EBRT of 60 s in BF1-P; IL of 89 g m(-3) h(-1) and EBRT of 90 s in BF2-C). A maximum EC of 52 g m(-3) h(-1) was obtained for the BTF (IL of 116 g m(-3) h(-1), EBRT of 45 s). Problems regarding high pressure drop appeared in the peat BF, whereas drying episodes occurred in the coconut fibre BF. DGGE revealed that the pure culture used for BF inoculation was not detected by day 105. Although two different inoculation procedures were applied, similar styrene removal at the end of the experiments was observed. The use as inoculum of activated sludge from municipal wastewater treatment plant appears a more feasible option.

摘要

使用两个分别填充泥炭和椰壳纤维的生物滤池(分别为BF1-P和BF2-C)以及一个填充塑料环的生物滴滤池(BTF)研究了苯乙烯的去除情况。采用了两种接种程序:BFs使用恶臭假单胞菌CECT 324菌株的富集培养物,BTF使用城市污水处理厂的活性污泥。施加的入口负荷(ILs)在10至45 g m(-3) h(-1)之间,空床停留时间(EBRTs)在30至120 s之间。在入口浓度为200至400 mg Nm(-3)的范围内,三个生物反应器的去除效率在70%至95%之间。BF1-P和BF2-C的最大去除能力(ECs)分别为81和39 g m(-3) h(-1)(BF1-P中IL为173 g m(-3) h(-1),EBRT为60 s;BF2-C中IL为89 g m(-3) h(-1),EBRT为90 s)。BTF的最大EC为52 g m(-3) h(-1)(IL为116 g m(-3) h(-1),EBRT为45 s)。泥炭生物滤池中出现了高压降问题,而椰壳纤维生物滤池中发生了干燥现象。变性梯度凝胶电泳(DGGE)显示,到第105天时未检测到用于BF接种的纯培养物。尽管采用了两种不同的接种程序,但在实验结束时观察到了相似的苯乙烯去除效果。使用城市污水处理厂的活性污泥作为接种物似乎是一个更可行的选择。

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