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Copper deficiency can limit nitrification in biological rapid sand filters for drinking water production

机译:铜缺乏会限制用于饮用水生产的生物快速砂滤器中的硝化作用

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Incomplete nitrification in biological filters during drinking water treatment is problematic, as it compromises drinking water quality. Nitrification problems can be caused by a lack of nutrients for the nitrifying microorganisms. Since copper is an important element in one of the essential enzymes in nitrification, we investigated the effect of copper dosing on nitrification in different biological rapid sand filters treating groundwater. A lab-scale column assay with filter material from a water works demonstrated that addition of a trace metal mixture, including copper, increased ammonium removal compared to a control without addition. Subsequently, another water works was investigated in full-scale, where copper influent concentrations were below 0.05 mu g Cu L-1 and nitrification was incomplete. Copper dosing of less than 5 mu g Cu L-1 to a full-scale filter stimulated ammonium removal within one day, and doubled the filter's removal from 0.22 to 0.46 g NH4-N m(-3) filter material h(-1) within 20 days. The location of ammonium and nitrite oxidation shifted upwards in the filter, with an almost 14-fold increase in ammonium removal rate in the filter's top 10 cm, within 57 days of dosing. To study the persistence of the stimulation, copper was dosed to another filter at the water works for 42 days. After dosing was stopped, nitrification remained complete for at least 238 days. Filter effluent concentrations of up to 13 mu g Cu L-1 confirmed that copper fully penetrated the filters, and determination of copper content on filter media revealed a buildup of copper during dosing. The amount of copper stored on filter material gradually decreased after dosing stopped; however at a slower rate than it accumulated. Continuous detection of copper in the filter effluent confirmed a release of copper to the bulk phase. Overall, copper dosing to poorly performing biological rapid sand filters increased ammonium removal rates significantly, achieving effluent concentrations of below 0.01 mg NH4-N L-1, and had a long-term effect on nitrification performance. (C) 2016 Elsevier Ltd. All rights reserved.
机译:在饮用水处理过程中,生物过滤器中的硝化不完全是一个问题,因为它会损害饮用水的质量。硝化问题可能由硝化微生物缺乏营养引起。由于铜是硝化中必不可少的酶之一的重要元素,因此我们研究了在不同的生物快速砂滤池中,铜剂量对硝化作用的影响。实验室规模的水厂过滤材料柱分析表明,与不含铜的对照相比,添加微量金属混合物(包括铜)可提高铵去除率。随后,对另一座自来水厂进行了大规模研究,铜进水浓度低于0.05μg Cu L-1,硝化作用不完全。向全尺寸过滤器投加少于5μg Cu L-1的铜,可在一天之内促进铵的去除,并使过滤器的去除率从0.22 g NH4-N m(-3)过滤材料h(-1)翻倍。在20天内。氨和亚硝酸盐氧化的位置在过滤器中向上移动,在用药57天之内,过滤器顶部10厘米的铵去除率几乎提高了14倍。为了研究刺激的持久性,在自来水厂将铜注入另一个过滤器中达42天。停止加药后,硝化作用至少要持续238天。过滤器流出物的浓度高达13μg Cu L-1,证实铜已完全渗透到过滤器中,并且测定过滤介质中的铜含量可显示出计量期间铜的堆积。停止添加后,过滤材料上存储的铜量逐渐减少;但是,其速度要比累积速度慢。连续检测过滤器废水中的铜,确认铜释放到本体相中。总体而言,向性能不佳的生物快速砂滤器投加铜可显着提高铵的去除率,使废水中的氨氮浓度低于0.01 mg NH 4-N L-1,并对硝化性能产生长期影响。 (C)2016 Elsevier Ltd.保留所有权利。

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