首页  |  本刊简介  |  编委会  |  投稿须知  |  订阅与联系  |  微信  |  出版道德声明  |  Ei收录本刊数据  |  封面
沸石悬浮填料生物移动床的亚硝化特性
摘要点击 2806  全文点击 1009  投稿时间:2021-04-16  修订日期:2021-06-18
查看HTML全文 查看全文  查看/发表评论  下载PDF阅读器
中文关键词  沸石悬浮填料  陶粒  亚硝化  生物移动床(MBBR)  高通量测序
英文关键词  zeolite-suspended packing  ceramsite  nitritation  moving bed biofilm reactor (MBBR)  high-throughput sequencing
作者单位E-mail
邓翠兰 华南理工大学环境与能源学院, 广州 510006
工业聚集区污染控制与生态修复教育部重点实验室, 广州 510006 
916624209@qq.com 
郭露 华南理工大学环境与能源学院, 广州 510006
工业聚集区污染控制与生态修复教育部重点实验室, 广州 510006 
 
汪晓军 华南理工大学环境与能源学院, 广州 510006
工业聚集区污染控制与生态修复教育部重点实验室, 广州 510006
佛山市化尔铵生物科技有限公司, 佛山 528300 
cexjwang@scut.edu.cn 
陈振国 佛山市化尔铵生物科技有限公司, 佛山 528300
华南理工大学化学与化工学院, 广州 510665 
 
中文摘要
      本研究以沸石为重要原料研制新型沸石悬浮填料,并将其用于启动沸石悬浮填料移动床反应器(ZMBBR),与装填普通陶粒的陶粒悬浮填料移动床(CMBBR)对比考察其亚硝化性能.结果表明:通过游离氨(FA)抑制的方法快速实现两种反应器的稳定亚硝化,两个反应器出水亚硝酸氮积累率均能达到90%以上;沸石对铵离子的吸附解吸作用使ZMBBR比CMBBR更快缓解FA对AOB的抑制,更有利于快速实现亚硝化;当ρ(NH4+-N)分别为350mg·L-1和1050 mg·L-1时,CMBBR与ZMBBR均能保持长期稳定的亚硝化,NPRAVG分别为0.43kg·(m3·d)-1和1.26kg·(m3·d)-1,ARE分别为82.21%和88.85%;进水ρ(NH4+-N)由250mg·L-1逐渐升至1250 mg·L-1过程中CMBBR的最大亚硝酸氮产率(NPRmax)仅为0.5634 kg·(m3·d)-1,进水ρ(NH4+-N)为750mg·L-1时,ρ(FA)为166mg·L-1,CMBBR受FA抑制崩溃;而ZMBBR的NPRmax可达1.800kg·(m3·d)-1,进水ρ(NH4+-N)为1250 mg·L-1时,反应器在ρ(FNA)达到峰值1.9611 mg·L-1后运行效果变差,随后ρ(FA)增至158mg·L-1,NPR大幅降至0.9028 kg·(m3·d)-1,ZMBBR运行效果显著变差.高通量测序表明,ZMBBR和CMBBR的优势菌群均为Nitrosomonas_europaea,相对丰度分别为11.15%和10.92%.
英文摘要
      A new type of zeolite-suspended packing was developed by using zeolite as an important raw material, which was then used to start the zeolite moving bed biofilm reactor (ZMBBR). ZMBBR was compared with the ceramsite moving bed biofilm reactor (CMBBR) packed with ordinary ceramsite-suspended packing to investigate the different nitritation performance. The results showed that stable nitritation was successfully achieved in two reactors by the inhibitory effect of free ammonia (FA), and both of their nitrite accumulation rates (NAR) reached 90%; due to the adsorption of zeolite to ammonium, ZMBBR relieved the inhibition of FA on AOB faster than CMBBR and achieved nitritation earlier; CMBBR and ZMBBR could maintain long-term stable nitrosation when ρ(NH4+-N) was 350 mg·L-1 and 1050 mg·L-1 and NPRAVG was 0.43 kg·(m3·d)-1 and 1.26 kg·(m3·d)-1, respectively, and ARECMBBR=82.21% and AREZMBBR=88.85%. In the process of the influent ρ(NH4+-N) gradually increasing from 250 mg·L-1 to 1250 mg·L-1, the maximum nitrite production rate (NPR) of CMBBR was 0.5634 kg·(m3·d)-1; when ρ(FA) reached 166 mg·L-1 at the influent ρ(NH4+-N) of 750 mg·L-1, CMBBR broke down for the heavy inhibition of FA. The maximum NPR of ZMBBR was 1.800 kg·(m3·d)-1, and the performance of ZMBBR was getting worse after the ρ(FNA) reached the peak value of 1.9611 mg·L-1 at the influent ρ(NH4+-N) of 1250 mg·L-1. Subsequently, the ρ(FA) of ZMBBR reached 158 mg·L-1 rapidly, the NPR dropped significantly to 0.9028 kg·(m3·d)-1, and the performance of ZMBBR became significantly worse. It was demonstrated by high-throughput sequencing analysis that the dominant strain of ZMBBR and CMBBR was Nitrosomonas_europaea, and the relative abundances of N._europaea in ZMBBR and CMBBR were 11.15% and 10.92%, respectively.

您是第75749651位访客
主办单位:中国科学院生态环境研究中心 单位地址:北京市海淀区双清路18号
电话:010-62941102 邮编:100085 E-mail: hjkx@rcees.ac.cn
本系统由北京勤云科技发展有限公司设计  京ICP备05002858号-2