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Engineering aspects and practical application of autotrophic nitrogen removal from nitrogen rich streams

机译:从富氮流中去除自养氮的工程方面和实际应用

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摘要

The anaerobicammoniumoxidation (Anammox) process, discovered 20 years ago, is, in combination withpartial nitritation, ideally suited to treat nitrogen rich waste water streams such as digester effluent.In this review the engineering aspects and the practical application of the process are reviewed. Theconventional nitrification–denitrification and nitritation–denitritation are also discussed briefly.The environmental conditions affecting the nitrification process, free ammonia and nitrous acid concentration,temperature, pH and dissolved oxygen concentration, are discussed. These conditions canbe controlled in such a way that the partial nitritation step produces an Anammox-suited influent. TheAnammox reactor conditions should favour the growth of the Anammox organisms in view of their lowgrowth rate and possible inhibition effects. Dissolved oxygen and nitrite concentrations should be keptas low as possible and biomass washout should be limited. If the partial nitritation process and the Anammoxprocessare occuring in the same reactor, care should be taken to the dissolved oxygen concentration,the ammonium load and the nitrite concentration to obtain a sustainable co-existence between aerobicand anaerobic ammonium oxidizers.An overview is presented of the practical implementation of autotrophic nitrogen removal. The processcan be accomplished in the same reactor (1-reactor system) or by using 2 separate reactors (2-reactorsystem). Typically the 1-reactor system is a biofilm or granular reactor where the ammonium oxidizersare active in the outer layers of the biofilm or granule, producing a suitable amount of nitrite for theAnammox organisms that are active in the inner layers. Transport of ammonium and the produced nitriteis governed by diffusion. Finally, the different nitrogen removal processes are compared in terms ofoperational conditions and a direction for future work is provided.
机译:20年前发现的厌氧铵氧化(Anammox)工艺与部分硝化相结合,非常适合处理诸如消化池废水等富氮废水流。本文综述了该工艺的工程方面和实际应用。还简要讨论了常规硝化-反硝化和硝化-亚硝化。讨论了影响硝化过程的环境条件,游离氨和亚硝酸浓度,温度,pH和溶解氧浓度。可以通过部分硝化步骤产生适合Anammox的进水的方式来控制这些条件。鉴于厌氧菌的低生长速率和可能的抑制作用,其条件应有利于厌氧菌的生长。溶解氧和亚硝酸盐的浓度应保持尽可能低,并且应限制生物质的洗脱。如果在同一反应器中发生部分硝化过程和厌氧氨氧化过程,则应注意溶解氧浓度,铵负载量和亚硝酸盐浓度,以实现好氧和厌氧铵氧化剂之间的可持续共存。实际实施自养脱氮。该过程可以在同一反应器(1-反应器系统)中或通过使用2个单独的反应器(2-反应器系统)完成。通常,1-反应器系统是生物膜或颗粒反应器,其中铵氧化剂在生物膜或颗粒的外层中具有活性,从而为在内层中具有活性的厌氧氨氧化菌产生适量的亚硝酸盐。铵的运输和所产生的亚硝酸盐受扩散控制。最后,根据操作条件对不同的脱氮工艺进行了比较,并提供了未来工作的方向。

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