栗浩亮, 徐继伟, 王传澍, 等. 外源氨氮输入对星云湖入湖区域表层沉积物-水界面氮迁移和交换通量的影响[J]. 自然保护地,2024,4(0):1−13. DOI: 10.12335/2096-8981.2024012001
引用本文: 栗浩亮, 徐继伟, 王传澍, 等. 外源氨氮输入对星云湖入湖区域表层沉积物-水界面氮迁移和交换通量的影响[J]. 自然保护地,2024,4(0):1−13. DOI: 10.12335/2096-8981.2024012001
LI H L, XU J W, WANG C S, et al. Effects of exogenous ammonia nitrogen on nitrogen transport and exchange fluxes at the surface sediment-water interface in the Xingyun Lake[J]. Natural Protected Areas, 2024, 4(0): 1−13. DOI: 10.12335/2096-8981.2024012001
Citation: LI H L, XU J W, WANG C S, et al. Effects of exogenous ammonia nitrogen on nitrogen transport and exchange fluxes at the surface sediment-water interface in the Xingyun Lake[J]. Natural Protected Areas, 2024, 4(0): 1−13. DOI: 10.12335/2096-8981.2024012001

外源氨氮输入对星云湖入湖区域表层沉积物-水界面氮迁移和交换通量的影响

Effects of exogenous ammonia nitrogen on nitrogen transport and exchange fluxes at the surface sediment-water interface in the Xingyun Lake

  • 摘要:
    目的 探明外源氨氮输入对云南高原湖泊入湖区域表层沉积物-水界面氮迁移和交换通量的影响。
    方法 以星云湖渔村河入湖区域表层沉积物为研究对象,硫酸铵(NH4)2SO4为外源氨氮,通过沉积物静态培养实验,开展不同浓度氨氮添加对沉积物-水界面氮交换通量的影响研究。实验中根据(NH4)2SO4溶液中N的质量浓度设置4个梯度实验组(4,8,16,32 mg/L)和1个空白对照组,培养周期为30 d。
    结果 星云湖渔村河入湖区域表层沉积物总氮(total nitrogen, TN)平均含量为2.95 g/kg,单因子污染指数(PTN)平均值为5.36,达到单因子污染指数评价标准中的重度污染级别,具有较高潜在生态风险;TN中可交换态氮(exchangeable nitrogen, EN)占比平均值为4.94 %,氮素迁移能力较强。实验周期内,沉积物中硝酸盐氮(NO3-N)的交换通量F(NO3-N)均为正数,表明NO3-N迁移特征表现为从沉积物向水体释放,且与外源输入氨氮浓度呈正相关,外源输入氨氮浓度越高,沉积物中NO3-N的释放量越大,反之越小;而氨氮(NH4+-N)的交换通量F(NH4+-N)在实验周期内由正数逐渐转为负数,最后趋向于零,表明NH4+-N迁移特征表现为先释放后沉淀,最后达到动态平衡状态。
    结论 高浓度的外源氨氮输入,短期内会促进沉积物中NO3-N的快速释放,使NO3-N在水体中不断累积,导致水质恶化,造成水体富营养化等环境问题。因此,未来应关注研究区域沉积物内源氮释放风险,进一步加强湖泊径流污染控制和综合治理,以降低氨氮输入引发的水环境问题。

     

    Abstract:
    Objectives To investigate the effects of exogenous ammonia nitrogen input on nitrogen transport and exchange fluxes at the surface sediment-water interface of the inflow area of Yunnan Plateau Lakes.
    Methods The surface sediment of the Xingyun Lake Fishery Village River inflow area was selected as the research object and (NH4)2SO4 was used as the exogenous ammonia nitrogen. Static sediment culture experiments were conducted to study the effects of different concentrations of ammonia nitrogen addition on nitrogen exchange flux at the sediment-water interface. The experiment was conducted with four gradient experimental groups (4, 8, 16, 32 mg/L) and one blank control group, with the mass concentration of nitrogen in the ammonium sulfate solution serving as the basis for the experimental design. The cultivation period was 30 days.
    Results The results indicated that the average total nitrogen (TN) content in the surface sediment of the Xingyun Lake Fishery Village River inflow area was 2.95 g/kg, with an average single-factor pollution index of 5.36, reaching the severe pollution level in the single-factor pollution index evaluation criteria, posing a high potential ecological risk. The proportion of exchangeable nitrogen (EN) in TN averages 4.94%, indicating a strong nitrogen migration capability. Throughout the experimental period, the exchange flux F(NO3-N) of nitrate nitrogen (NO3-N) in the sediment was consistently positive, indicating a migration characteristic of NO3-N releasing from sediment to water, positively correlated with the concentration of exogenous input ammonia nitrogen (NH4+-N). The higher the concentration of exogenous input NH4+-N, the greater the release of NO3-N from sediment, and vice versa. On the other hand, the exchange flux F(NH4+-N) of NH4+-N gradually changes from positive to negative during the experimental period, ultimately approaching zero, indicating a migration characteristic of ammonia nitrogen being released initially and then precipitated, eventually reaching a dynamic equilibrium state.
    Conclusions The rapid release of NO3-N from sediment in response to high concentrations of exogenous NH4+-N input can result in the continuous accumulation of NO3-N in the water body. This accumulation can result in a deterioration of water quality and the emergence of environmental issues such as eutrophication and algal blooms. Consequently, in the future, it would be prudent to devote attention to the potential for endogenous nitrogen release from sediment in the study area. Further efforts should be made to reinforce the control and comprehensive management of lake runoff pollution to mitigate the water environmental problems caused by NH4+-N input.

     

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