首页> 外文会议>WEFTEC 2001;Annual conference exposition of Water Environment Federation >COMBINING EXISTING TRICKLING FILTER TREATMENT WITHNITROGEN REMOVAL TECHNOLOGY: OPTIMIZING A MODIFIEDSINGLE –SLUDGE NITRIFICATION-DENITRIFICATION SYSTEM
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COMBINING EXISTING TRICKLING FILTER TREATMENT WITHNITROGEN REMOVAL TECHNOLOGY: OPTIMIZING A MODIFIEDSINGLE –SLUDGE NITRIFICATION-DENITRIFICATION SYSTEM

机译:将现有的滴滤滤池处理与脱氮技术相结合:优化改性的污泥-硝化-硝化-除氮系统

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The Pennsylvania State University Wastewater Treatment Plant (PSU WWTP) treatsrnabout 3 MGD of wastewater from the University and part of the Borough of StaternCollege. All treated effluent is discharged to land application. Increasing nitrate levels inrngroundwater under the land application fields caused concern because groundwater is thernmajor drinking water supply in the area, and there is a maximum contaminant level forrnnitrate of 10 mg/L as N in drinking water. This led to the plant being upgradedrn(retrofitted) to include nitrogen removal from the wastewater. As part of the retrofit, newrnsingle-sludge nitrification-denitrification (SSND) activated sludge treatment (anoxic andrnaerobic suspended growth reactors) was combined with existing stone-media tricklingrnfilters resulting in a unique treatment process flow scheme. This paper presents therndesign and operational criteria for this modified single-sludge nitrification-denitrificationrnprocess, and reports the results of an extensive optimization study performed at the plant.rnIn the treatment process, primary effluent flow is split between trickling filters and thernanoxic reactor (the primary effluent flow going to the anoxic tank is called the tricklingrnfilter bypass, for the purposes of this paper). Flows exiting the trickling filters and thernanoxic tank are then recombined prior to flowing to aerobic reactors and finalrnclarification. An internal mixed liquor recycle (IMLR) recirculates mixed liquor andrnnitrate from the aerobic reactors to the anoxic reactor. By utilizing the two existingrntrickling filters to remove BOD and nitrify part of the flow, it was possible to use existingrntanks for aeration, even though the hydraulic detention time in the tanks is only 4 hours,rnrather than the 6 to 8 hours of detention time normally required for nitrification ofrnmunicipal wastewater. Plus, it reduces the oxygen (and air) requirements by about 50%,rnsaving on operating costs.rnFollowing start-up of the new process, the effluent total nitrogen often exceeded therntarget of 10 mg/L, and an optimization study was performed to maximize nitrogenrnremoval. The two variables studied for optimization were the trickling filter bypass flowrnand the IMLR flow rate. Bypass flow rates of 10%, 30%, and 50%, and IMLR flow ratesrnof 1Q, 2Q, and 3Q, were investigated. Maximum nitrogen removal was achieved at arntrickling filter bypass flow of 50% of the influent flow, and an IMLR flow rate of 2Qrn(two times the influent flow rate). This mode of operation reduced the total nitrogen byrn75% to approximately 8.5 mg/L (with a relatively low standard deviation of 1.8).
机译:宾夕法尼亚州立大学废水处理厂(PSU WWTP)处理来自大学和StaternCollege自治市一部分的废水约3 MGD。所有处理过的废水都排放到土地上。在土地应用领域,地下水中硝酸盐含量的增加引起了人们的关注,因为地下水是该地区最主要的饮用水供应,并且饮用水中作为硝酸盐的最大污染物硝酸盐含量为10 mg / L。这导致工厂进行了升级(改造),包括从废水中去除氮。作为改造的一部分,将新型单污泥硝化-反硝化(SSND)活性污泥处理(缺氧和厌氧的悬浮生长反应器)与现有的石质介质滴滤池组合在一起,形成了独特的处理工艺流程。本文介绍了这种改进的单污泥硝化-硝化反硝化工艺的设计和操作标准,并报告了工厂进行的广泛优化研究的结果。在处理过程中,主要污水流在滴滤池和热氧反应器之间分离(主要就本文而言,进入缺氧池的废水流称为滴流滤池旁路。然后,从滴流式过滤器和热氧罐出来的流会重新混合,然后流入有氧反应器并进行最终澄清。内部混合液再循环(IMLR)将混合液和硝酸盐从好氧反应器再循环到缺氧反应器。通过利用两个现有的滴滤池去除BOD并硝化部分水流,即使罐中的水力滞留时间仅为4小时,而不是通常的6至8个小时,也可以使用现有的坦克进行曝气。硝化市政废水所需。另外,它可以将氧气(和空气)需求降低约50%,从而节省运营成本。rn在新工艺启动后,废水中的总氮通常超过了10 mg / L的目标,并进行了优化研究以最大限度地去除氮。为优化而研究的两个变量是滴滤器旁路流量和IMLR流量。研究了10%,30%和50%的旁路流量以及1Q,2Q和3Q的IMLR流量。在点滴滤池旁通流量为进水流量的50%,IMLR流量为2Qrn(进水流量的两倍)时,可以实现最大的氮去除率。这种操作方式将总氮减少了75%,降至约8.5 mg / L(相对标准偏差为1.8)。

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