首页> 外文期刊>Journal of Water and Environment Technology >Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems
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Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems

机译:尼罗罗非鱼水产养殖系统淡水污泥和生物絮凝物中的反硝化和硝酸盐异化还原(DNRA)活性

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Suspended organic sludge from freshwater and biofloc Nile tilapia systems were examined for the presence of denitrifying and dissimilatory nitrate reduction to ammonium (DNRA) activities under nitrate and sulfide stimulation. Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the freshwater sludge and biofloc samples to simulate low and high nitrate levels that are normally found in aquaculture systems. The results showed that freshwater sludge and biofloc both had denitrifying activity immediately after nitrate addition. However, ammonium accumulated in the biofloc reactors but not in the freshwater reactors, indicating the activity of DNRA in the high C/N biofloc particles. The influence of sulfide on nitrate reduction was also studied by adding different concentrations of sulfide along with 100 mg NO3--N/L. The results showed that elevated sulfide concentrations partially inhibited denitrification in the freshwater sludge and caused nitrite and ammonium accumulation, in which ammonium formation was probably responsible by DNRA activity. In sulfide-added biofloc reactors, ammonium accumulated at the same level as found in the biofloc reactors without sulfide. Therefore, DNRA bacteria residing in the biofloc aquaculture system were more likely to be heterotrophs that did not use sulfide as their electron donor.
机译:检查了淡水和生物絮凝物尼罗罗非鱼系统中悬浮的有机污泥在硝酸盐和硫化物刺激下是否存在反硝化和异化硝酸盐还原成铵(DNRA)活性。将25和100 mg NO 3 - -N / L的初始硝酸盐浓度添加到淡水污泥和生物絮凝剂样品中,以模拟通常在水中发现的低和高硝酸盐水平水产养殖系统。结果表明,添加硝酸盐后,淡水污泥和生物絮凝物均具有反硝化活性。但是,铵聚集在生物絮凝反应器中,而不是在淡水反应器中积聚,表明DNRA在高C / N生物絮凝剂颗粒中的活性。还通过添加不同浓度的硫化物以及100 mg NO 3 - -N / L来研究硫化物对硝酸盐还原的影响。结果表明,升高的硫化物浓度部分抑制了淡水污泥中的反硝化作用,并导致亚硝酸盐和铵盐的积累,其中铵的形成可能是DNRA活性的原因。在添加硫化物的生物絮凝反应器中,铵的累积水平与没有硫化物的生物絮凝反应器中的水平相同。因此,存在于生物絮凝水产养殖系统中的DNRA细菌更可能是不使用硫化物作为其电子供体的异养生物。

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