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首页> 外文期刊>Water Research >Elimination of micropollutants and transformation products from a wastewater treatment plant effluent through pilot scale ozonation followed by various activated carbon and biological filters
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Elimination of micropollutants and transformation products from a wastewater treatment plant effluent through pilot scale ozonation followed by various activated carbon and biological filters

机译:通过中试规模的臭氧氧化,然后进行各种活性炭和生物过滤器,消除废水处理厂废水中的微量污染物和转化产物

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摘要

Conventional wastewater treatment plants are ineffective in removing a broad range of micropollutants, resulting in the release of these compounds into the aquatic environment, including natural drinking water resources. Ozonation is a suitable treatment process for micropollutant removal, although, currently, little is known about the formation, behavior, and removal of transformation products (TP) formed during ozonation. We investigated the elimination of 30 selected micropollutants (pharmaceuticals, X-ray contrast media, industrial chemicals, and TP) by biological treatment coupled with ozonation and, subsequently, in parallel with two biological filters (BF) or granular activated carbon (GAC) filters. The selected micropollutants were removed to very different extents during the conventional biological wastewater treatment process. Ozonation (specific ozone consumption: 0.87 +/- 0.29 g(03) g(DOG)(-1) hydraulic retention time: 17 +/- 3 min) eliminated a large number of the investigated micropollutants. Although 11 micropollutants could still be detected after ozonation, most of these were eliminated in subsequent GAC filtration at bed volumes (BV) of approximately 25,000 m(3) m(-3). In contrast, no additional removal of micropollutants was achieved in the BF. Ozonation of the analgesic tramadol led to the formation of tramadol-N-oxide that is effectively eliminated by GAC filters, but not by BF. For the antiviral drug acyclovir, the formation of carboxy-acyclovir was observed during activated sludge treatment, with an average concentration of 3.4 +/- 1.4 mu g L-1 detected in effluent samples. Subsequent ozonation resulted in the complete elimination of carboxy-acyclovir and led to the formation of N-(4-carbamoyl-2-imino-5oxo imidazolidin)-formamido-N-methoxyacetetic acid (COFA; average concentration: 2.6 +/- 1.0 mu g L-1). Neither the BF nor the GAC filters were able to remove COFA. These results highlight the importance of considering TP in the evaluation of advanced wastewater treatment processes. The results further indicate that post-treatment of ozonated wastewater with GAC filtration seems to be more suitable than BF, due to the sorption of formed TP to the activated carbon. (c) 2016 Elsevier Ltd. All rights reserved.
机译:传统的废水处理厂无法有效去除多种微量污染物,导致这些化合物释放到包括天然饮用水资源在内的水生环境中。臭氧化是用于去除微污染物的合适处理方法,尽管目前对臭氧化过程中形成的转化产物(TP)的形成,行为和去除知之甚少。我们研究了通过生物处理与臭氧化作用并随后与两个生物过滤器(BF)或颗粒状活性炭(GAC)过滤器并行进行的消除30种选定的微污染物(药物,X射线造影剂,工业化学品和TP)的方法。在常规的生物废水处理过程中,选定的微量污染物的去除程度差别很大。臭氧化(特定的臭氧消耗量:0.87 +/- 0.29 g(03)g(DOG)(-1)的水力停留时间:17 +/- 3分钟)消除了许多研究的微污染物。尽管在臭氧处理后仍可检测到11种微污染物,但在随后的GAC过滤中,床体积(BV)约为25,000 m(3)m(-3)时,大多数污染物已被消除。相反,在高炉中没有实现微量污染物的额外去除。止痛曲马多的臭氧化导致形成曲马多-N-氧化物,GAC过滤器有效地消除了该作用,但高炉无此作用。对于抗病毒药无环鸟苷,在活性污泥处理过程中观察到了羧基无环鸟苷的形成,在废水样品中检测到的平均浓度为3.4 +/- 1.4μg L-1。随后的臭氧化作用导致羧基阿昔洛韦的完全消除,并导致形成N-(4-氨基甲酰基-2-亚氨基-5氧代咪唑烷)-甲酰胺基-N-甲氧基乙酸(COFA;平均浓度:2.6 +/- 1.0微米g L-1)。 BF和GAC过滤器均无法去除COFA。这些结果突出了在评估高级废水处理过程中考虑使用TP的重要性。结果进一步表明,由于形成的TP吸附在活性炭上,采用GAC过滤对臭氧化废水进行后处理似乎比BF更合适。 (c)2016 Elsevier Ltd.保留所有权利。

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