首页> 外国专利> AERATED REMOVAL OF NITROGEN POLLUTANTS FROM BIOLOGICALLY DEGRADABLE WASTEWATERS

AERATED REMOVAL OF NITROGEN POLLUTANTS FROM BIOLOGICALLY DEGRADABLE WASTEWATERS

机译:曝气去除生物可降解废水中的氮污染物

摘要

A cyclic activated sludge method and apparatus uses multi-reactor facilities (typically 2, 3, 4, or multiples of 2, e.g., 6, 8, 12, 16, etc.), without separate secondary clarifiers, to accommodate a continuous hydraulic profile. Each reactor is configured with an admixture volume as an initial unaerated mixing zone followed by repetitive mixing gradients to nucleate and promote large activated sluge floc sizes followed by a second intermittently aerated hydraulically connected reaction zone using partial baffle walls. The second reaction zone in each reactor is collectively, but out of phase, operated with successive air-on and air-off sequences. The air-off sequence enables solids-liquid separation and a depletion of biomass oxidation reduction potential to take place after an air-on sequence, with subsequent withdrawal of a fraction of the reactor upper level liquid contents using a variable rate moving box weir decanter. Sludge containing heterotrophic and autotrophic micro-organisms is directed from the second zone to the initial volume for admixture with biodegradable wastewaters containing more than 3:1 parts of BOD:TKN. The period of each air-on sequence depends upon the relative oxygen demanding mass load input. There is provision for influent flow during an extended air-off sequence after removal of the supernatant fraction. The air-on sequence typically operates with filling of influent into the reactor. Air-on sequencing in the second reactor volume is used to mix and elevate the oxidation reduction potential of the settled separated microbial culture from negative to mixed positive values. Air-off sequencing in the second reactor volume provides separated liquid-solids phases with a dynamic depletion to negative oxidation reduction potential (about -150 mV reference hydrogen electrode).
机译:循环活性污泥方法和设备使用多反应器设施(通常为2、3、4或2的倍数,例如6、8、12、16等),而无需单独的二级澄清池,以适应连续的水力状况。每个反应器配置有混合物体积作为初始无气混合区,然后进行重复混合梯度以成核并促进较大的活性污泥絮凝物尺寸,然后通过使用部分挡板壁的第二个间歇充气的水力连接反应区进行配置。每个反应器中的第二个反应区共同进行,但异相,以连续的通气和通气顺序进行操作。排气顺序使得能够在通气顺序之后进行固液分离和生物质氧化还原潜力的消耗,随后使用可变速率移动箱堰倾析器抽出一部分反应器上层液体内容物。将含有异养和自养微生物的污泥从第二区引导至初始体积,以便与含有超过3:1份BOD:TKN的可生物降解废水混合。每个通气顺序的周期取决于所需的相对氧气质量负荷输入。在去除上清液部分后,在延长的排气过程中有进水。空气顺序通常在将流入物填充到反应器中的情况下进行。第二反应器体积中的空气测序用于混合沉降的分离微生物培养物的氧化还原电位,并将其从负值提高到混合正值。在第二反应器体积中的排气顺序提供了分离的液相-固相​​,其动态消耗至负氧化还原电位(约-150mV参考氢电极)。

著录项

  • 公开/公告号SI20157A

    专利类型

  • 公开/公告日2000-08-31

    原文格式PDF

  • 申请/专利权人 BISASCO PTY. LIMITED;

    申请/专利号SI19980020017

  • 发明设计人 GORONSZY MERVYN CHARLES;

    申请日1998-01-09

  • 分类号C02F3/12;C02F3/30;C02F101/16;

  • 国家 SI

  • 入库时间 2022-08-22 01:55:07

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