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首页> 外文期刊>RSC Advances >Nutrient removal and microbial mechanisms in constructed wetland microcosms treating high nitrate/nitrite polluted river water
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Nutrient removal and microbial mechanisms in constructed wetland microcosms treating high nitrate/nitrite polluted river water

机译:耐湿地微观植物治疗高硝酸盐/亚硝酸盐污染河水的营养去除和微生物机制

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In rivers, nitrate/nitrite concentrations often vary with seasons and locations, and excess nitrogen can cause eutrophication. Constructed wetlands (CWs) have been used as a typical and optimal ecological technology to purify river water. In the present study, nitrogen (N) removal and related microbial mechanisms of treating high nitrate/nitrite polluted river water were explored in CW microcosms. Excellent removal performances were simultaneously achieved with low and stable effluent concentrations of NO _(3) ~(?) –N (0.29–0.51 mg L ~(?1) ), NO _(2) ~(?) –N (0.65–1.0 mg L ~(?1) ), NH _(4) ~(+) –N (0.18–0.40 mg L ~(?1) ), and TN (1.24–1.56 mg L ~(?1) ) in our experimental and control groups. Based on the mass balance approach, plant uptake eliminated 11–14% of the total N input and sediment storage contributed 5–11% of N removal, indicating assimilation into biomass and sediment might be important sections of N removal besides microbial nitrification and denitrification. According to the 16S rRNA gene sequencing results, nitrate had positive effects on microbial community richness and diversity. Proteobacteria were particularly identified to be the dominant bacterial strains involved in N transformation in CWs and accounted for 37.26–52.99%. The relative abundance of Proteobacteria was highest after adding nitrate. Gamma- and beta- Proteobacteria were probably responsible for nitrate biodegradation. Bacillus and Cyanobacteria were speculated to be responsible for N removal and transformation. Overall, the results in this study could provide suggestions for treating high nitrate/nitrite polluted river water.
机译:在河流中,硝酸盐/亚硝酸盐浓度通常随季节和位置而变化,过量的氮气会导致富营养化。被建造的湿地(CWS)被用作典型和最佳的生态技术来净化河水。在本研究中,在CW Microcosms中探讨了在CW Microcosms中探讨了处理高硝酸盐/亚硝酸盐污染河水的氮气(n)去除和相关的微生物机制。通过NO _(3)〜(α)-N(0.29-0.51mg L〜(α1)),NO _(2)〜(α)-N(0.65 -1.0mg l〜(α1)),NH _(4)〜(+)-N(0.18-0.40mg L〜(α1))和TN(1.24-1.56mg l〜(?1))我们的实验和对照组。基于质量平衡方法,植物摄取消除了11-14%的总输入和沉积物储存的5-11%的N次去除,表明除了微生物硝化和反硝化之外的N去除的重要部分。根据16S RRNA基因测序结果,硝酸盐对微生物群落丰富和多样性具有积极影响。特别鉴定出蛋白质体细菌是CWS中N转化的显性细菌菌株,并占37.26-52.99%。加入硝酸盐后,蛋白菌的相对丰度最高。 γ-和β-植物可能对硝酸盐生物降解负责。推测芽孢杆菌和青霉菌是负责N去除和转化。总体而言,该研究的结果可以提供治疗高硝酸盐/亚硝酸盐污染的河水的建议。

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