生物增效结合SBR-AO处理垃圾渗滤液

孙铁刚, 孙翼虎. 生物增效结合SBR-AO处理垃圾渗滤液[J]. 环境工程学报, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
引用本文: 孙铁刚, 孙翼虎. 生物增效结合SBR-AO处理垃圾渗滤液[J]. 环境工程学报, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
Sun Tiegang, Sun Yihu. Treatment of landfill leachate by combining bioaugmentation and SBR-AO[J]. Chinese Journal of Environmental Engineering, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
Citation: Sun Tiegang, Sun Yihu. Treatment of landfill leachate by combining bioaugmentation and SBR-AO[J]. Chinese Journal of Environmental Engineering, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744

生物增效结合SBR-AO处理垃圾渗滤液

  • 基金项目:

    湖南省环保科研课题项目,湘财建指〔2014〕287号

  • 中图分类号: X703.1

Treatment of landfill leachate by combining bioaugmentation and SBR-AO

  • Fund Project:
  • 摘要: 在渗滤液处理现场进行了生物增效结合SBR-AO处理垃圾渗滤液的中试实验,对试验各段和整体工艺的运行条件和处理能力进行了测试分析:SBR段经过生物增效后,对NH3-N和BOD5的去除率分别达到89.0%和80.8%,明显优于未增效前的去除率。AO段试验结果显示,O池DO达到3.0 mg/L以上,经过生物增效可达最大NH3-N去除能力;A池硝化液回流比R值达到1.2时,系统的脱氮能力最大,而R值在0.4之内时,系统的去除COD能力达到最大。整体运行结果显示,当SBR-AO系统以脱氮为目的,系统对NH3-N的去除率可达98.8%,对TN的去除率可达82.6%;当SBR-AO系统以去除COD为目的,BOD5去除率可达94.0%,COD的去除率68.0%。
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出版历程
  • 收稿日期:  2015-02-03
  • 刊出日期:  2015-07-02
孙铁刚, 孙翼虎. 生物增效结合SBR-AO处理垃圾渗滤液[J]. 环境工程学报, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
引用本文: 孙铁刚, 孙翼虎. 生物增效结合SBR-AO处理垃圾渗滤液[J]. 环境工程学报, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
Sun Tiegang, Sun Yihu. Treatment of landfill leachate by combining bioaugmentation and SBR-AO[J]. Chinese Journal of Environmental Engineering, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744
Citation: Sun Tiegang, Sun Yihu. Treatment of landfill leachate by combining bioaugmentation and SBR-AO[J]. Chinese Journal of Environmental Engineering, 2015, 9(7): 3345-3349. doi: 10.12030/j.cjee.20150744

生物增效结合SBR-AO处理垃圾渗滤液

  • 1. 湖南迪亚环境工程有限公司, 长沙 410007
基金项目:

湖南省环保科研课题项目,湘财建指〔2014〕287号

摘要: 在渗滤液处理现场进行了生物增效结合SBR-AO处理垃圾渗滤液的中试实验,对试验各段和整体工艺的运行条件和处理能力进行了测试分析:SBR段经过生物增效后,对NH3-N和BOD5的去除率分别达到89.0%和80.8%,明显优于未增效前的去除率。AO段试验结果显示,O池DO达到3.0 mg/L以上,经过生物增效可达最大NH3-N去除能力;A池硝化液回流比R值达到1.2时,系统的脱氮能力最大,而R值在0.4之内时,系统的去除COD能力达到最大。整体运行结果显示,当SBR-AO系统以脱氮为目的,系统对NH3-N的去除率可达98.8%,对TN的去除率可达82.6%;当SBR-AO系统以去除COD为目的,BOD5去除率可达94.0%,COD的去除率68.0%。

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