School of Geographic and Oceanographic Sciences, Nanjing University, Nanjing 210023, China.
Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China.
Int J Environ Res Public Health. 2018 Nov 16;15(11):2568. doi: 10.3390/ijerph15112568.
Understanding spatio-temporal differences in nitrogen (N) transformation, transport and reduction rates in water bodies is critical to achieve effective mitigation of river eutrophication. We performed culture experiments in six rivers in the Taihu Basin using a custom made in-situ experimental apparatus. We investigated spatio-temporal differences in reduce processes and rates of different N forms and assessed the contribution of biological processes to dissolved inorganic N (DIN) reduce. Results showed that biological processes played a major role in N reduction in summer, while non-microbial processes were dominant in winter. We observed significant spatial and temporal differences in the studied mechanisms, with reduction rates of different N compounds being significantly higher in summer and autumn than spring and winter. Reduction rates ranged from 105.4 ± 25.3 to 1458.8 ± 98.4 mg·(m³·d) for total N, 33.1 ± 12.3 to 440.9 ± 33.1 mg·(m³·d) for ammonium, 56.3 ± 22.7 to 332.1 ± 61.9 mg·(m³·d) for nitrate and 0.4 ± 0.3 to 31.8 ± 9.0 mg·(m³·d) for nitrite across four seasons. Mean DIN reduction rates with and without microbial activity were 96.0 ± 46.4 mg·(m³·d) and 288.1 ± 67.8 mg·(m³·d), respectively, with microbial activity rates accounting for 29.7% of the DIN load and 2.2% of the N load. Results of correlation and principal component analysis showed that the main factors influencing N processing were the concentrations of different N forms and multiple environmental factors in spring, N concentrations, DO and pH in summer, N concentrations and water velocity in autumn and N concentrations in winter.
了解水体中氮(N)转化、迁移和还原速率的时空差异对于实现河流富营养化的有效缓解至关重要。我们使用定制的原位实验装置在太湖流域的六条河流中进行了培养实验。我们研究了不同 N 形态的还原过程和速率的时空差异,并评估了生物过程对溶解无机氮(DIN)还原的贡献。结果表明,生物过程在夏季的 N 还原中起主要作用,而在冬季则是非微生物过程占主导地位。我们观察到研究机制存在显著的时空差异,不同 N 化合物的还原速率在夏季和秋季显著高于春季和冬季。总氮的还原速率范围为 105.4 ± 25.3 至 1458.8 ± 98.4 mg·(m³·d),铵态氮为 33.1 ± 12.3 至 440.9 ± 33.1 mg·(m³·d),硝酸盐为 56.3 ± 22.7 至 332.1 ± 61.9 mg·(m³·d),亚硝酸盐为 0.4 ± 0.3 至 31.8 ± 9.0 mg·(m³·d),跨越四个季节。有和没有微生物活性的 DIN 还原平均速率分别为 96.0 ± 46.4 mg·(m³·d)和 288.1 ± 67.8 mg·(m³·d),微生物活性速率分别占 DIN 负荷的 29.7%和 N 负荷的 2.2%。相关和主成分分析的结果表明,春季影响 N 处理的主要因素是不同 N 形态的浓度和多种环境因素,夏季是 N 浓度、DO 和 pH,秋季是 N 浓度和水速,冬季是 N 浓度。