首页> 外文会议>WEFTEC 2012;Water Environment Federation annual technical exhibition and conference >Extending the Modeling of High Purity Oxygen Wastewater Treatment Processes: Transition from Closed to Open Basin Operations – A Full Scale Case Study
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Extending the Modeling of High Purity Oxygen Wastewater Treatment Processes: Transition from Closed to Open Basin Operations – A Full Scale Case Study

机译:扩展高纯氧废水处理过程的模型:从封闭流域到开放流域的过渡–大规模案例研究

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About 15% of municipal wastewater treatment in the United States is carried out usinghigh purity oxygen (HPO) wastewater treatment processes (Praxair, 2011). HPO systemsenable compact process footprint, produce good settling sludge, good DO control,process flexibility and low VOC emissions (Jiang et al, 2010). First generation HPOsystems have completely covered basins, and the oxygen feed is charged directly to theheadspace. A surface aerator sprays liquid droplets into the headspace, and the oxygendiffuses into the water droplets and is incorporated into the bulk liquid. However, closedbasin high purity oxygen systems can have a limited capacity for Nitrification (Metcalf &Eddy, 2003; Sears et al, 2003; Randall & Cokgor, 2001) mainly due to the accumulationof CO_2 in the headspace which could lead to depressed pH in the process and Nitrifiergrowth inhibition. Second generation HPO systems are operated in uncovered activatedsludge basins, hence avoiding the issue of headspace CO_2 accumulation and enablingeffective Biological Nutrient Removal (BNR).A number of first generation HPO wastewater systems have been upgraded to enhancetheir BNR capabilities (Randall & Cokgor, 2001). The application of biological processmodeling tools can enable the cost effective evaluation of upgrade and retrofit options(Henze, et al, 2000). While robust and reliable process modeling tools exist forconventional aeration systems, there are few options available for modeling pure oxygenbased processes (Tzeng et al, 2003). Because of the differences in the oxygen transferefficiency, vent gas volumes, gas exchange characteristics, CO_2 stripping conditions, andoff gas volume controlled evaporative cooling effect between conventional aeration andpure oxygen based systems, extensions to the traditional ASM models are necessary toadequately model HPO operations. Even within HPO systems, closed vs. open basinHPO operations also vary, especially with regards to CO_2 accumulation in the headspacein closed basin systems, with implications for biological process modeling.In this study, we describe the application of Hydromantis’ GPS-X? platform to enablethe effective modeling of open basin pure oxygen systems using data from a full scalepure oxygen activated sludge plant that was retrofit from closed to open basin pureoxygen operations.
机译:在美国,约有15%的市政废水处理是使用高纯氧(HPO)废水处理工艺进行的(Praxair,2011)。 HPO系统可实现紧凑的过程足迹,产生良好的沉淀污泥,良好的DO控制,过程灵活性以及低VOC排放(Jiang等,2010)。第一代HPO系统具有完全覆盖的水盆,氧气进料直接装到顶部空间。表面曝气器将液滴喷入顶部空间,氧气扩散到液滴中并混入本体液体中。然而,密闭式高纯氧系统的硝化能力有限(Metcalf&Eddy,2003; Sears等,2003; Randall&Cokgor,2001),这主要是由于顶部空间中的CO_2积累会导致过程中pH降低。和硝化作用抑制作用。第二代HPO系统在未覆盖的活性污泥池中运行,从而避免了顶空CO_2积累的问题并实现了有效的生物营养去除(BNR)。许多第一代HPO废水系统已进行升级以增强其BNR能力(Randall&Cokgor,2001) 。生物过程建模工具的应用可以对升级和改造选项进行经济有效的评估(Henze等,2000)。尽管存在常规曝气系统强大而可靠的过程建模工具,但建模纯氧基过程的方法却很少(Tzeng等,2003)。由于常规曝气和纯氧基系统之间的氧气传输效率,排气量,气体交换特性,CO_2汽提条件和废气量控制的蒸发冷却效果之间存在差异,因此有必要对传统ASM模型进行扩展以对HPO操作进行充分建模。即使在HPO系统中,封闭盆地与开放盆地的HPO操作也有所不同,特别是在封闭盆地系统的顶部空间中的CO_2积聚方面,这对生物过程建模具有重要意义。在这项研究中,我们描述了Hydromantis GPS-X的应用。该平台可使用全规模纯氧活化污泥厂的数据(从密闭式操作改为敞口式纯氧操作进行改造),对敞口式纯氧系统进行有效建模。

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