氮氧同位素解析堤垸地表水硝酸盐来源

Identification of Nitrate Source in Polder Surface Water by Nitrogen and Oxygen Isotopes

  • 摘要: 堤垸是滨湖、滨江低洼地带的一种重要景观,农业面源污染已成为其主要的环境问题之一. 为解析堤垸地区地表水硝酸盐污染来源,以洞庭湖屈原垸平江河段为研究对象,采用稳定同位素及水化学分析方法定性识别污染来源,并结合MixSIAR模型量化不同污染源的贡献率. 结果表明:①硝态氮和氨氮是屈原垸平江河段地表水无机氮的主要赋存形态,时间上,硝态氮浓度在丰、枯水期间无显著差异(p>0.05),而丰水期氨氮浓度平均值高于枯水期;空间上,垸内硝态氮浓度显著低于垸外(p<0.01),而氨氮浓度显著高于垸外(p<0.01). ②MixSIAR模型结果表明,化肥、土壤有机氮、水产养殖废水、粪肥和污水是研究区地表水硝酸盐的主要来源,对丰水期地表水中硝酸盐的贡献率分别为33.0%、32.6%、19.4%和11.7%,对枯水期的贡献率分别为26.7%、31.2%、21.5%和16.9%,而大气沉降对地表水中硝酸盐来源贡献较小,仅为3.5%. ③研究区地表水硝酸盐转化过程主要以硝化作用为主,未发生明显的反硝化过程. 研究显示,研究区地表水硝酸盐污染主要受农业面源污染的影响,污染物主要来源于土壤有机氮、化肥及水产养殖废水,硝酸盐污染防治应考虑化肥使用效率和水产养殖废水处理.

     

    Abstract: Polder is an important part of the landscape pattern in low-lying areas along lakes and rivers. Inorganic nitrogen pollution in surface water has become a serious environmental issue in the polder area. To identify the sources of nitrate pollution in the polder area, the Pingjiang River section of the Quyuan Polder of Dongting Lake was selected as the study area. Stable isotope and water chemistry analysis methods were used to qualitatively identify the pollution sources, and the MixSIAR model was used to quantify the contributions of different pollution sources. The results showed that: (1) Nitrate nitrogen and ammonia nitrogen were the main forms of inorganic nitrogen in surface water of the Pingjiang River section of Quyuan Polder. Temporally, there was no significant difference in nitrate nitrogen concentration between wet and dry seasons (p>0.05), while the average concentration of ammonia nitrogen value was higher in wet season than in dry season. Spatially, nitrate nitrogen concentration inside the polder was significantly lower than outside (p<0.01), while ammonia nitrogen concentration was significantly higher than outside (p<0.01). (2) Nitrogen and oxygen isotopes and the analysis results of the MixSIAR model confirmed that chemical fertilizers, soil organic nitrogen, aquaculture wastewater, manure and sewage were the main sources of nitrate in surface water of the study area. The contributions of these nitrogen sources to nitrate were 33.0%, 32.6%, 19.4% and 11.7%, respectively in the wet season, and 26.7%, 31.2%, 21.5% and 16.9% respectively in the dry season. Atmospheric deposition contributed only 3.5% of nitrate sources in surface water. (3) The nitrate transformation process in the study area was mainly nitrification, and no significant denitrification process was observed. The study shows that nitrate pollution in surface water of the study area is mainly affected by agricultural non-point source pollution, and the pollutants primarily come from soil organic nitrogen, chemical fertilizers, and aquaculture wastewater. Therefore, to prevent and control nitrate pollution, we should consider improving fertilizer efficiency and treating aquaculture wastewater.

     

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