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Microbial nitrogen transformation potential in surface run-off leachate from a tropical landfill

机译:热带垃圾填埋场地表径流渗滤液中微生物氮的转化潜力

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Ammonium is one of the major toxic compounds and a critical long-term pollutant in landfill leachate. Leachate from the Jatibarang landfill in Semarang, Indonesia, contains ammonium in concentrations ranging from 376 to 929 mg N L~(-1). The objective of this study was to determine seasonal variation in the potential for organic nitrogen ammonification, aerobic nitrification, anaerobic nitrate reduction and anaerobic ammonium oxidation (anammox) at this landfilling site. Seasonal samples from leachate collection treatment ponds were used as an inoculum to feed synthetic media to determine potential rates of nitrogen transformations. Aerobic ammonium oxidation potential (<0.06 mg N L~(-1) h~(-1)) was more than a hundred times lower than the anaerobic nitrogen transformation processes and organic nitrogen ammonification, which were of the same order of magnitude. Anaerobic nitrate oxidation did not proceed beyond nitrite; isolates grown with nitrate as electron acceptor did not degrade nitrite further. Effects of season were only observed for aerobic nitrification and anammox, and were relatively minor: rates were up to three times higher in the dry season. To completely remove the excess ammonium from the leachate, we propose a two-stage treatment system to be implemented. Aeration in the first leachate pond would strongly contribute to aerobic ammonium oxidation to nitrate by providing the currently missing oxygen in the anaerobic leachate and allowing for the growth of ammonium oxidisers. In the second pond the remaining ammonium and produced nitrate can be converted by a combination of nitrate reduction to nitrite and anammox. Such optimization of microbial nitrogen transformations can contribute to alleviating the ammonium discharge to surface water draining the landfill.
机译:铵是垃圾渗滤液中的主要有毒化合物之一,也是长期的关键污染物。来自印度尼西亚三宝垄Jatibarang垃圾填埋场的渗滤液中铵盐的浓度范围为376至929 mg N L〜(-1)。这项研究的目的是确定该填埋场的有机氮氨化,好氧硝化,厌氧硝酸盐还原和厌氧铵氧化(厌氧氨)潜力的季节变化。来自渗滤液收集处理池的季节性样品用作接种物,以饲喂合成培养基,以确定潜在的氮转化率。好氧铵氧化电位(<0.06 mg N L〜(-1)h〜(-1))比相同数量级的厌氧氮转化过程和有机氮氨化过程低一百倍以上。除亚硝酸盐外,厌氧硝酸盐的氧化没有进行。以硝酸盐为电子受体生长的分离株不会进一步降解亚硝酸盐。仅在需氧硝化和厌氧氨氮中观察到季节的影响,并且影响相对较小:在干旱季节,发生率高达三倍。为了从渗滤液中完全去除过量的铵,我们建议实施两阶段处理系统。通过在厌氧渗滤液中提供当前缺少的氧气并允许铵氧化剂的生长,第一个渗滤液池中的曝气将大大促进好氧铵氧化为硝酸盐。在第二个池塘中,剩余的铵和产生的硝酸盐可通过硝酸盐还原的组合转化为亚硝酸盐和厌氧氨水。微生物氮转化的这种优化可以有助于减轻铵排放到填埋场的地表水。

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