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楠溪江硝态氮来源定量识别及其不确定性分析
引用本文:纪晓亮,舒烈琳,陈铮,梅琨,许凤冉,白音包力皋,Mendes Ana,张明华,商栩.楠溪江硝态氮来源定量识别及其不确定性分析[J].中国环境科学,2021,41(8):3784-3791.
作者姓名:纪晓亮  舒烈琳  陈铮  梅琨  许凤冉  白音包力皋  Mendes Ana  张明华  商栩
作者单位:1. 温州医科大学公共卫生与管理学院, 浙江省流域水环境与健康风险研究重点实验室, 浙江 温州 325035;2. 中国水利水电科学研究院, 流域水循环模拟与调控国家重点实验室, 北京 100038;3. 埃武拉大学, 葡萄牙 埃武拉 7002554
基金项目:国家自然科学基金资助项目(51979197);欧盟资助项目(PI/2017/388-178);温州市基础性科研项目(S20180005);温州医科大学人才科研启动基金资助项目(QTJ18032)
摘    要:选择温州市楠溪江流域为研究区,通过水化学分析和硝态氮中氮氧稳定同位素示踪技术,对水体硝态氮时空分布特征、迁移转化过程和污染来源进行识别,结合稳定同位素源解析模型(SIAR),定量识别不同污染源的贡献率,并在此基础上应用概率统计方法对模拟结果的不确定性进行分析.结果表明:研究区水体氮素赋存形态以硝态氮为主;硝态氮含量呈现明显的时空变化,时间上,丰水期硝态氮浓度高于枯水期,空间上,支流硝态氮浓度高于主河道;硝化作用主导了流域内硝态氮的转化过程,化肥、土壤有机氮和粪便污水是楠溪江水体硝态氮的主要来源;SIAR模型计算显示大气沉降、化肥、土壤有机氮、粪便污水对枯水期水体硝态氮的贡献率分别为3.0%~12.9%,25.5%~32.7%,28.7%~36.2%和24.7%~37.5%,对丰水期水体硝态氮贡献率为2.5%~14.3%,28.5%~40.0%,28.8%~39.7%和18.9%~29.90%.模拟结果的不确定性分析表明SIAR模拟结果存在一定程度的不确定性,不同污染源贡献率的不确定性从大到小排序为:土壤有机氮>化肥>粪便污水>大气沉降.

关 键 词:楠溪江  稳定同位素  硝态氮污染  污染源识别  不确定性分析  
收稿时间:2020-12-24

Quantitative identification of riverine nitrate sources and uncertainty analysis in the Nanxi River
JI Xiao-liang,SHU Lie-lin,CHEN Zheng,MEI Kun,XU Feng-ran,Baiyinbaoligao,MENDES Ana,ZHANG Ming-hua,SHANG Xu.Quantitative identification of riverine nitrate sources and uncertainty analysis in the Nanxi River[J].China Environmental Science,2021,41(8):3784-3791.
Authors:JI Xiao-liang  SHU Lie-lin  CHEN Zheng  MEI Kun  XU Feng-ran  Baiyinbaoligao  MENDES Ana  ZHANG Ming-hua  SHANG Xu
Institution:1. Key Laboratory of Watershed Science and Health of Zhejiang Province, School of Public Health and Management, Wenzhou Medical University, Wenzhou 325035, China;2. State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, China Institute of Water Resources and Hydropower Research, Beijing 100038, China;3. Evora University, Evora 7002554, Portugal
Abstract:Accurate identification of nitrate sources is the key step for effectively mitigate riverine nitrate pollution. In this study, the Nanxi River watershed located in Wenzhou city was selected as the research area. Hydrochemical analysis and nitrogen and oxygen stable isotopes in nitrate were used to identify spatio-temporal variation, migration and transformation, and pollution sources of nitrate. Then, combining the stable isotope analysis in R (SIAR) model to quantitatively identify the contributions for different pollution sources. On this basis, the probabilistic method was employed to analyze the uncertainty of modelling results. Nitrate was the main form of nitrogen in this study area; there existed significant spatio-temporal variation of riverine nitrate content, temporally, the nitrate concentration in wet season was higher than that in dry season, spatially, the nitrate concentration in tributary was higher than that in main stream. Microbial nitrification was the primary nitrogen transformation process within the Nanxi River watershed, chemical nitrogen, soil organic nitrogen and manure and sewage were the main contributors of nitrate to the river; SIAR modeling revealed that the contributions of atmospheric deposition, chemical nitrogen, soil organic nitrogen, and manure and sewage were 3.0%~12.9%, 25.5%~32.7%, 28.7%~36.2%, and 24.7%~37.5%, respectively, in the dry season, and 2.5%~14.3%, 28.5%~40.0%, 28.8%~39.7%, and 18.9%~29.9%, respectively, in the wet season. The uncertainty analysis demonstrated that uncertainties existed in some extent during nitrate source identification, the uncertainty for different sources followed:soil organic nitrogen > chemical nitrogen > manure and sewage > atmospheric deposition.
Keywords:Nanxi River  stable isotope  nitrate pollution  pollution source identification  uncertainty analysis  
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