液晶面板工业尾水深度处理中试
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  • 英文篇名:ADVANCED TREATMENT OF LIQUID CRYSTAL DISPLAY INDUSTRIAL TAIL WATER IN A PILOT SCALE SYSTEM
  • 作者:衷从强 ; 张建 ; 朱军 ; 胡蓉 ; 朱霜月 ; 尹魁浩 ; 彭盛华
  • 英文作者:ZHONG Cong-qiang;ZHANG Jian;ZHU Jun;HU Rong;ZHU Shuang-yue;YIN Kui-hao;PENG Sheng-hua;State Environmental Protection Key Laboratory of Drinking Water Source Management and Technology,Shenzhen Key Laboratory of Drinking Water Source Safety Control,Shenzhen Research Academy of Environmental Sciences;Productivity Centre of Jiangsu Province;
  • 关键词:立体生态污水处理系统 ; 液晶面板工业尾水 ; 深度处理 ; 中试
  • 英文关键词:ecological-biological combined process;;liquid crystal display industrial tail water;;advanced treatment;;a pilot scale research
  • 中文刊名:HJGC
  • 英文刊名:Environmental Engineering
  • 机构:深圳市环境科学研究院国家环境保护饮用水水源地管理技术重点实验室深圳市饮用水水源地安全保障重点实验室;江苏省生产力促进中心;
  • 出版日期:2018-05-22
  • 出版单位:环境工程
  • 年:2018
  • 期:v.36;No.239
  • 基金:深圳市科技应用示范项目(KJYY20150430175426620);; 深圳市技术攻关项目(JSGG20160301165934501)
  • 语种:中文;
  • 页:HJGC201805007
  • 页数:5
  • CN:05
  • ISSN:11-2097/X
  • 分类号:36-40
摘要
深圳市某液晶面板工业尾水具有机物浓度低、硝态氮及总氮含量高、BOD5/COD值<0.1的特点。现应用立体生态污水处理技术对该尾水进行中试规模深度处理。运行90 d后,反应池表面水生植物生长状况良好,填料及植物根系微生物挂膜情况较佳,微生物量较大。COD、氨氮、硝态氮和总氮去除率分别为63%、48%、55%和68%,其中,硝态氮和总氮去除率比现有实际深度处理工艺出水分别高35和45百分点。对中试进出水进行GC-MS分析得出,尾水中部分含氮杂环有机物得到降解,并生成其他有机中间产物。
        Secondary effluent from a liquid crystal display( LCD) industrial wastewater treatment plant in Shenzhen contains low concentration organic matter,high concentration nitrate and total nitrogen,and its BOD5/COD was even lower than 0. 1.Pilot scale ecological-biological combined system was applied to treat the LCD tail water for reuse. After 90-day operation,the aquatic plants grew well,the microbial biomass on filler and plant roots was large. In addition,COD,ammonia,nitrate and total nitrogen( TN) removal efficiencies reached up to 63%,48%,55% and 68%,respectively. The nitrate and TN removal efficiencies were 35% and 45% higher than that of the advanced treatment plant. Using GC-MS analysis,several nitrogenous heterocyclic compounds were degraded and several organic intermediates appeared in the effluent.
引文
[1]黄民生.略论地下水硝酸盐氮污染及其防治措施[J].上海环境科学,1995,14:26-27.
    [2]黄袁金.FBR工艺应用于污水处理厂工艺提标升级改造[J].能源环境保护,2016,30(3):28-30.
    [3]程恒卫,张景成,张彦平,等.FBR工艺处理生活污水试验研究[J].水处理技术,2008,34(2):74-77.
    [4]Wang T,Zhang H M,Yang F L,et al.Start-up and long-term operation of the anammox process in a fixed bed reactor(FBR)filled with novel non-woven ring carriers[J].Chemosphere,2013,91(5):669-675.
    [5]刘雯,丘锦荣,卫泽斌,等.植物-生物膜氧化沟处理生活污水的中试研究[J].中国给水排水,2009,25(15):8-11.
    [6]方雨.BFBR立体生态处理技术在市政污水处理厂改造工程中的应用[J].中国高新技术企业,2017,10:117-118.
    [7]Gao M L,Song W H,Zhang J Y,et al.Effect on enzymes and histopathology in earthworm(Eisenia foetida)induced by triazole fungicides[J].Environmental Toxicology and Pharmacology,2013,35:427-433.
    [8]Hong J M,Hua M M,Sun R,et al.Unraveling characteristics of nutrient removal and microbial community in a novel aerated landscape:Activated sludge ecological system[J].Bioresource Technology,2016,212:280-288.
    [9]Ekama G A,Wentzel M C.Denitrification kinetics in biological N&P removal activated sludge systems treating municipal wastewaters[J].Water Science and Technology,1999,39(6):69-77.
    [10]吴光学,魏楠,时运红,等.反硝化生物膜工艺污水深度脱氮研究进展[J].中国给水排水,2014,30(22):72-77.

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