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铁改性石英砂过滤协同控制饮用水含氮消毒副产物和条件致病菌
摘要点击 2060  全文点击 602  投稿时间:2021-06-11  修订日期:2021-07-17
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中文关键词  铁改性石英砂(Fe-sand)  含氮消毒副产物(N-DBPs)  条件致病菌  胞外多聚物  微生物群落
英文关键词  iron-modified quartz sand  nitrogenous disinfection by-products  opportunistic pathogens  extracellular polymer substances  microbial community
作者单位E-mail
齐鹏 广州大学大湾区环境研究院, 珠江三角洲水质安全与保护教育部重点实验室, 广州 510006 1642700757@qq.com 
胡春 广州大学大湾区环境研究院, 珠江三角洲水质安全与保护教育部重点实验室, 广州 510006
中国科学院生态环境研究中心饮用水科学与技术重点实验室, 北京 100085 
 
邢学辞 广州大学大湾区环境研究院, 珠江三角洲水质安全与保护教育部重点实验室, 广州 510006 xcxing@gzhu.edu.cn 
毕志浩 广州大学大湾区环境研究院, 珠江三角洲水质安全与保护教育部重点实验室, 广州 510006  
李泽松 广州大学大湾区环境研究院, 珠江三角洲水质安全与保护教育部重点实验室, 广州 510006  
中文摘要
      石英砂在给水工艺中最主要的作用为去除浊度,其固-液界面的微生物作用受到忽视.为了解决普通石英砂(sand)在控制消毒副产物和条件致病菌有限的问题,将普通石英砂改性为铁改性石英砂(Fe-sand),用气相色谱-ECD测定了典型含氮消毒副产物(N-DBPs)和含碳消毒副产物的最大生成势.结果表明,Fe-sand对卤代硝基甲烷,卤乙酰胺和卤乙腈生成的抑制效果分别提升了51.51%、43.66%和90.6%.此外,基于定量qPCR检测了Hartmanella vermiformisLegionella spp.、Mycobacterium spp.、M.aviumNaegleria spp.的基因拷贝数,发现Fe-sand对条件致病菌同样有显著地抑制作用.Fe-sand对NOM的去除提升能力有限,但Fe-sand滤料表面生物膜分布较为均匀、不易脱落且更稳定,其出水悬浮态生物膜则较难聚集,胞外蛋白α螺旋二级结构消失,因而极容易被氯穿透,有效抑制了出水中生物膜对N-DBPs和条件致病菌的持续贡献.Fe-sand固-液界面显著改变了微生物群落和悬浮生物膜的形态,对保障饮用水水质安全提供了新的思路,对水厂现有工艺的提升和改造起到良好的理论支撑作用.
英文摘要
      The main function of quartz sand in drinking water treatment has been to remove turbidity, while the microbial effect of its solid-liquid interface has been ignored. In order to solve the limitations of control of the disinfection by-products (DBPs) and opportunistic pathogens (OPs) in common quartz sand, the common quartz sand was modified to iron sand. The maximum DBPs formation potential of typical nitrogenous disinfection by-products (N-DBPs) and carbonaceous disinfection by-products was determined using gas chromatography-ECD. Compared with those of sand, the inhibition effects of halonitromethanes, haloacetamides, and haloacetonitriles by the Fe-sand were increased by 51.51%, 43.66%, and 90.6%, respectively. In addition, the gene copy numbers of Hartmanella vermiformis, Legionella spp., Mycobacterium spp., M. avium, and Naegleria spp. were detected via quantitative qPCR, and the results indicated that the Fe-sand did have a similar significant inhibitory effect on OPs. The Fe-sand had limited ability to enhance the removal of NOM. However, the Fe-sand effectively inhibited the continuous contribution of biofilm to N-DBPs and opportunistic pathogens. The distribution of biofilms on the surface of the Fe-sand filter media was uniform, not likely to fall off, and more stable; however, the suspended biofilms in the effluent were more difficult to aggregate. In addition, the α-helix of the secondary structure in the extracellular protein disappeared in the effluent of the Fe-sand. Therefore, the whole suspended biofilm was easily penetrated by chlorine. The Fe-sand solid-liquid interface did significantly change the microbial community structure and suspended biofilm characteristics, which provides a new concept to ensure the safety of drinking water quality and plays a good theoretical supporting role in the improvement and transformation of the existing process in drinking water treatment plants.

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